ML093340221
| ML093340221 | |
| Person / Time | |
|---|---|
| Site: | Susquehanna, Bell Bend  |
| Issue date: | 05/06/2005 |
| From: | Shriver B PPL Bell Bend, Susquehanna |
| To: | Office of New Reactors |
| Shared Package | |
| ML093270273 | List: |
| References | |
| BNP-2009-356 | |
| Download: ML093340221 (166) | |
Text
Brltt T.
Brltt T. McKinney McKinney PPL Susquehanna, PPL Susquehanna, LLC LLC Vice President-Nudear Vice President-Nudear Site Site Operations Operations 769 Salem 769 Salem Boulevard Boulevard Berwick, PA Berwick, PA 18603 18603 Tel. 570.542.3149 Tel. 570.542.3149 Fax Fax 570.542.1504 570.542.1504 btmckinney@pplweb.com btmckinney@pplweb.com MAY 062005 MAY 062005 U. S. Nuclear U. S. Nuclear Regulatory Regulatory Commission Commission Attn: Document Attn: Document Control Control Desk Desk Mail Station Mail Station OPI-17 OPI-17 Washington, DC Washington, DC 20555 20555 SUSQUEHANNA SUSQUEHANNA STEAM STEAM ELECT~C STATION STATION RADIOLOGICAL ENVIRONMENTAL ANNUAL RADIOLOGICAL ANNUAL ENVIRONMENTAL OPERATING REPORT OPERATING REPORT Docket Nos.
Docket Nos. 50-387 50-387 PLA-5894 PLA-5894 and 50-388 and 50-388 The Susquehanna SES The Susquehanna SES Annual Annual Radiological Radiological Environmental Environmental OperatingOperating Report Report is is hereby submitted hereby submitted forfor the the calendar calendar year year 2004 2004 in in accordance accordance with with Technical Technical Specification Section Specification Section 5.6.2.
5.6.2.
If you have If you have any any questions, questions, please contact Mr.
please contact Mr. Rocco Rocco R. R. Sgarro, Sgarro, Manager, Manager, Nuclear Nuclear Regulatory Affairs Regulatory Affairs atat (610)
(610) 774-7552.
774-7552.
Sincerely, Sincerely, Attachments Attachments copy: Mr.
copy: A. J.
Mr. A. J. Blarney, Blarney, NRCNRC Sr. Sr. Resident Resident Inspector Inspector Mr. S.
Mr. S. J.
J. CoIlins, CoIlins, NRC NRC Region Region I, I, Regional Regional Administrator Administrator J. T.
Mr. J.
Mr. T. Furia, Furia, NRC NRC Region Region I, I, Senior Senior Health Health Physicist Physicist Mr. R.
Mr. R. V.
V. Guzman, Guzman, NRC NRC Project Project Manager Manager Mr. R.
Mr. R. Janati, Janati, DEPIBRP DEPIBRP
Susq'lJ~ta'~I""astean1
- Electfl'~;Station * .
,,~"~~
Units Units 1;;'~'&2 *f (.~-.'
2004 ANNUAL 2004 ANNUAL <REPORT
<REPORT ..
Annual Annual Radiological Radiological tt Environmental Environmental
,, ~"-."~7~.~.__ __ ~._ .. .. ,~ Op~r~~ln.g p.grtt ~.
...'.~:::: ;~_:c::;, ':.~.... >.~. ,;.~.. ':;~ ;;.... '.~. ~>~;~.~,e p.gr
SUSQUEHANNA SUSQUEHANNA STEAM STEAM ELECTRIC ELECTRIC STATION STATION
\J UNITS 11 and UNITS and 22 Annual Radiological Annual Radiological Environmental Operating Environmental Operating Report Report January 11 Through January Through December December 31, 31, 2004 2004 Prepared by:
Prepared by:
.. Reviewed Reviewed by:
by:
R. E.
R. Doebler, Chemistry E. Doebler, Chemistry Support Support Supervisor Supervisor -- SSES SSES B. E.
B. E. Rhoads, Rhoads, Manager Manager -- Plant Plant Chemistry Chemistry PPL Susquehanna,llC PPL Susquehanna,llC 769 Salem 769 Salem Boulevard Boulevard Berwick. Pennsylvania Berwick. Pennsylvania 18603 18603 rr
.. ii
TABLE OF TABLE OF CONTENTS CONTENTS
SUMMARY
AND
SUMMARY
AND CON~USIONS ........................................................................................
........................................................................................ 11 INTRODUCTION ......................................................................................................................
INTRODUCTION ......................................................................................................................6 6 AMBIENT RADIATION AMBIENT RADIATION MONITORING MONITORING ..............................................................................
.............................................................................. 1717 PATIiWA AQUATIC PATIiW AQUATIC AY Y MONITORING MONITORING ................................................................................
................................................................................ 2121 A'lMOSPHERIC PATIiW A'lMOSPHERIC PATIiWAY AY MONITORING MONITORING ..............................................................
.......34 34
'TERRES1RIAL PATHWAY
'TERRES1RIAL PATHWAY MONITORING MONITORING .......................................................................
.......................................................................38 38 GROUND WA1'ER GROUND WA1'ER MONITORING MONITORING .......................................................................................
.......................................................................................43 43 REF'ERENCES .........................................................................................................
REF'ERENCES ......................................................................................................... ::.............. 45
..............45 APPENDICES APPENDICES A.
A. 2004 REMP SAMPLE 2004 REMP SAMPLE COLLECfION, COLLECfION, ANALYSIS ANALYSIS TYPE, TYPE, A-I A-I ANALYTICAL METHODS, ANALYTICAL METHODS, PROGRAM PROGRAM CHANGES CHANGES AND AND EXCEPTIONS EXCEPTIONS B.
~
B. 2004 REMP 2004 REMP MONITORING MONITORING SCHEDULE SCHEDULE (SAMPLING (SAMPLING AND AND ANALYSIS)
ANALYSIS) B-1 B-1 C.
C. 2004 REMP 2004 REMP MONITORING MONITORING LOCATION LOCATION DESCRIPTIONSDESCRIPTIONS C-l C-l
\..../
\..../
D.
D. 2004 LAND 2004 LAND USE USE CENSUS CENSUS RESULTS RESULTS D-I D-I E.
E. INTENTIONAlLY LEFf INTENTIONAlLY LEFf BLANK BLANK E-l E-l F.
F. INTENTIONAlLY LEFf INTENTIONAlLY LEFf BLANKBLANK F-l F-l G.
G. 2004 SSES 2004 SSES REMP REMP
SUMMARY
SUMMARY
OF OF DATA DATA G-l G-l H.
H. COMPARISON OF COMPARISON OF INDICATOR INDICATOR AND AND CONTROL CONTROL 2004 2004 H-l H-l REMP ANNUAL MEANS REMP ANNUAL MEANS FOR FOR SELECTED SELECTED MEDIA MEDIA ANALYSIS RESULTS ANALYSIS RESULTS WITH WITH MEANS MEANS FROM FROM PREOPERATIONAL AND PREOPERATIONAL AND PRIOR PRIOR OPERATIONAL OPERATIONAL PERIODS PERIODS 1.
- 1. SPECIFIC ANALYSIS RESULTS SPECIFIC ANALYSIS RESULTS TABULATED TABULATED BY BY MEDIA MEDIA I-I I-I AND SAMPLING AND SAMPLING PERIOD PERIOD J.
J. PERFORMANCE
SUMMARY
PERFORMANCE
SUMMARY
FOR FOR THE THE RADIORADIO ANAL ANALYSES YSES OF OF 1-1 1-1 SPIKED ENVIRONMENTAL SAMPLE SPIKED ENVIRONMENTAL SAMPLE 1v1EDIA 1v1EDIA -- 2004 2004
LIST OF LIST OF FIGURES FIGURES
\J
\J Figure Figure Numbers Numbers Title Title Page Page 1.
- 1. Exposure Pathways Exposure Pathways toto Humans Humans 10 10 2.
- 2. 2004 no Monitoring 2004 no Monitoring Locations Locations within within One One Mile Mile of of the the SSES SSES 11 11 3.
- 3. 2004 no Monitoring 2004 no Monitoring Locations Locations fromfrom One One toto Five Five Miles Miles of of the the 12 12 SSES SSES 4.
- 4. 2004 TLD Monitoring 2004 TLD Monitoring Locations Locations Greater Greater than than Five Mi1es from Five Mi1es from the the 13 13 SSES SSES 5.
- 5. 2004 Environmental 2004 Environmental Sampling Sampling Locations Locations within within One One Mile Mile of of the the 14 14 SSES SSES 6.
- 6. 2004 Environmental Sampling 2004 Environmental Sampling Locations Locations from from One One to to Five Five Miles Miles of of 'IS
\"._/
\"._/ 7.
- 7. 2004 Environmental 2004 Environmental Sampling Sampling Locations Locations Greater Greater than than Five Five Miles Miles 16 16 from the SSES from the SSES 8.
- 8. Ambient Radiation Ambient Radiation Leve]s Leve]s Based Based on no Data on no Data 20 20 9.
- 9. Gross Beta Gross Beta Activity Activity in in Surface Surface Water Water 31 31 10.
- 11. Gross Beta Gross Beta Activity Activity in in Drinking Drinking Water Water 33 33 12.
- 12. Gross Beta Gross Beta Activity Activity in in Air Air Particulates Particulates 37 37 13.
- 13. Iodine-131 Activity Iodine-131 Activity in in Milk Milk 42 42 iiii
- Radiological Dose Radiological
SUMMARY
AND
SUMMARY
Dose Impact Impact AND CONCLUSIONS CONCLUSIONS This report on This report on the the Radiological Radiological of SSES had of SSES had no no adverse adverse radiological radiological Environmental Monitoring Environmental Monitoring Program Program impact on impact on thethe health health and and safety safety of of the the covers the covers the period period January January 1, 1, 2004 2004 public or public or the the environment.
environment.
through December through December 31, 31 , 2004.
2004.
The total whole The total whole body body dose dose from from both both During that During that period, period, 1388 1388 analyses analyses were were ingested radionuclides ingested radionuclides and and direct direct performed on performed on 850 850 samples samples at at 3737 radiation from radiation from SSES SSES Operations Operations is is sampling locations.
sampling locations. Additionally, Additionally, 253 253 negligible compared negligible compared to to the the public's public's TLD direct TLD direct radiation measurements radiation measurements exposure from exposure from natural natural background background were performed were performed at at 58 58 locations locations around around radiation, medical radiation, medical irradiation, irradiation, and and the site.
the site. radiation from radiation from consumer consumer productsproducts of of more than more than 300300 milliremlyear milliremlyear effective effective In assessing all In assessing all the the data data gathered gathered and and dose-equivalent.
dose-equivalent.
comparing with comparing with SSES SSES pre-operational pre-operational data, it it was was concluded concluded that that thethe operation data, operation The following graph The following graph compares compares public public dose from dose from SSESSSES operation operation to to that that from from other sources other sources of of radioactivity radioactivity and and radiation.
radiation.
COMPARISON COMPARISON OF OF PERCENT PERCENT OF OF AVERAGE AVERAGE ANNUAL PUBLIC ANNUAL PUBLIC EFFECTIVE EFFECTIVE DOSE- DOSE-EQUIVALENT FROM EQUIVALENT FROM OTHER OTHER SOURCES SOURCES WITH WITH THAT FROM THAT FROM THE THE SSES SSES Nat ural Background Natural 81%
81%
~s
<0.01
<0.01 5%
5%
Medical Medical 14%
14%
Sources for Sources for the the values values provided, provided, with with the the exception exception of of Susquehanna, Susquehanna, are are the the following following from from NCRP Rep ort #93 NCRP Report #93 (1987):
(1987): Tables Tables 2.4 2.4 (Natural (Natural Background),
Background), 5.1 (Consumer Products),
5.1 (Consumer Products), and and 7.4 (M 7.4 (Medical).
edical).
- 2004 Radiological 2004 Radiological Environmental Environmental MonitoringMonitoring Report Report 1 1
cOl
Summary and Conclusions pathway pathway to to man.
man. The The maximum maximum dose dose Ambient Gamma Ambient Gamma Radiation Radiation from the from the ingestion ingestion ofof tritium tritium was was estimated at estimated at the the nearest nearest downriver downriver Environmental Environmental directdirect radiation radiation municipal water municipal water supplier supplier via via the the measurements were measurements were performed performed quarterly quarterly drinking water drinking water pathway pathway andand near near the the on and on and around around thethe SSES SSES sitesite using using outfall of outfall of the the SSES SSES discharge discharge to to the the thermoluminescent dosimeters thermoluminescent dosimeters (TLDs).(TLDs). Susquehanna River Susquehanna River via via the the fish fish pathway. The pathway. The maximum maximum wholewhole body body The maximum direct The maximum direct radiation radiation dose dose and organ and organ doses doses due due to to tritium tritium identified identified from SSES from SSES operation operation to to aa member member of of via REMP via REMP samples samples isis approximately approximately the public the public was was approximately approximately 0.0388 0.0388 0.0015 mremlyear.
0.0015 mremlyear. ThisThis dose dose isis less less mrem for mrem for all all of2004.
of2004. This This dose dose than one-tenth than one-tenth ofof one one percent percent ofof the the represents approximately represents approximately 0.16% 0.16% of of the the dose guidelines dose guidelines stated stated in in 10 10 CFR CFR 50,50, 25-mrem whole-body 25-mrem whole-body SSES SSES Technical Technical Appendix 1.
Appendix 1.
Requirements (TRO Requirements (TRO 3.11.3) 3.11.3) limit limit for for all all SSES sources SSES sources ofof radioactivity radioactivity and and radiation.
radiation.
Aquatic Environment Aquatic Environment Surface water and Surface water and drinking drinking waterwater samples were samples were analyzed analyzed for for concentrations of concentrations of gross gross beta, beta, tritium, tritium, iodine-I3l, and iodine-I3l, and gamma gamma emitting emitting nuclides. Drinking nuclides. Drinking waterwater samples samples were were also analyzed also analyzed for for concentrations concentrations of of gross alpha gross alpha Gross Gross alpha alpha andand betabeta activities detected activities detected werewere consistent consistent with with those reported those reported in in previous previous years.
years.
Iodine-I31 activity was Iodine-I31 activity was detected detected in 10 in 10 of36 surface of36 surface water water samples.
samples. The The activity was activity was slightly slightly above above the the MDC.
MDC.
Evidence indicates Evidence indicates thatthat it it is is there there only only as the as the result result of of the the discharge discharge of of medical medical waste to waste to the the Susquehanna Susquehanna or or Lackawanna Rivers Lackawanna Rivers through through sewage sewage treatment plants treatment plants upstream upstream of of the the SSES.
SSES.
Iodine-I31 was Iodine-I31 was notnot reported reported to to have have been discharged been discharged with with water water released released from the from the SSES SSES to to the the Susquehanna Susquehanna River during River during 2004.
2004.
Tritium activity Tritium activity attributable attributable to to SSES SSES operation was detected operation was detected in in the the aquatic aquatic 2
2 2004 Radiological 2004 Radiological Environmental Environmental Monitoring Monitoring Report Report
Summary' and Summary' and Conclusions Conclusions Fish samples were Fish samples were analyzed analyzed for for concentrations of concentrations of gamma gamma emitting emitting Cow milk samples Cow milk samples were were analyzed analyzed forfor nuclides. Concentrations nuclides. Concentrations of of naturally naturally concentrations ofiodine-131 concentrations ofiodine-131 as as well well as as occurring K-40 occurring K-40 were were consistent consistent withwith other gamma other gamma emittipg emittipg nuclides.
nuclides. AllAll those detected those detected inin previous previous years.
years. No No iodine results iodine results were were less less than than the the MDC.
MDC.
fission or fission or activation activation products products werewere Concentrations of Concentrations of naturally naturally occumng' occumng' detected in detected in fish.
fish. K-40 were K-40 were consistent consistent with with those those detected in detected in previous previous years.
years. N~ fission fission or or Sediment samples were Sediment samples were analyzed analyzed for for activation products activation products \vere
\vere detected.
detected.
concentrations of concentrations of gamIIla gamIIla emitting emitting nuclides. Cesium-137 nuclides. Cesium-137 was was observed observed in in Potatoes were briefly Potatoes were briefly irrigated irrigated atat one one
sediment and sediment and attributed attributed to to non-SSES non-SSES location in location in June June 2004 2004 using using sources (residual sources (residual fallout fallout from from Susquehanna River Susquehanna River water.
water. These These were were atmospheric weapons atmospheric weapons testing).
testing). .. sampled during sampled during thethe harvest harvest season season and and Concentrations of Concentrations of naturally naturally occurring occurring analyzed for analyzed for concentrations concentrations of of gamma gamma K-40, radium-226, K-40, radium-226, and and actinium-actinium- emitting nuclides.
emitting nuclides. Concentrations Concentrations of of ..
thorium-228 were thorium-228 were found found consistent consistent with with miturally occumng miturally occumng K-40 K-40 were were found found those detected those detected inin previous previous years.
years. consistent with consistent with those those in in previous previous years.
years.
No fission No fission or or activation activation products products were were Atmospheric Environment Atmospheric Environment detected.
detected.
Air particulate samples Air particulate samples were were analyzed analyzed Ground 'Vater' Ground 'Vater' for concentrations for concentrations of of gross gross beta beta and and ..
gamma emitting gamma emitting nuclides.
nuclides. Cosmogenic Cosmogenic .. Ground water samples Ground water samples were were analyzed analyzed Be-7 was Be-7 was detected detected at at levels levels consistent consistent for concentrations for concentrations oftrithini oftrithini arid arid gamma gamma with those with those detected detected in in previous previous years.
years. emitting nuclides.
emitting nuclides. Tritium Tritium activity activity above MDC above MDC was was detected detected in in 11 of of 36 36 Air iodine samples Air iodine samples werewere analyzed analyzed for for samples at samples at control control location location 12F3.
12F3. NoNo concentrations of concentrations of iodine-131.
iodine-131. All All results results fission or fission or activation activation products products were were were less were less than than the the MDC.
MDC. detected.
detected.
Terrestrial Environment Terrestrial Environment Soil samples were Soil samples were analyzed analyzed 'for 'for concentrations of concentrations of gamma gamma emitting emitting ..
nuclides. Cesium-137 nuclides. Cesium-137 was was observed observed in in soil and soil and attributed attributed to to non-SSES non-SSES sources sources (residual fallout (residual fallout from from atmospheric atmospheric weapons testing).
weapons testing). Concentrations Concentrations of of naturally occurring naturally occurring K-40K-40 werewere consistent with consistent with those those detected detected in in previous years.
previous years. Concentrations Concentrations of of naturally occurring naturally occurring radium-226, radium-226, and and actinium-thorium-228 were actinium-thorium-228 were consistent consistent V
V with those with those ofof previous previous years.
years.
2004 Radiological 2004 Radiological Environmental Environmental Monitoring Monitoring Report Report 33
Summary and Summary and Conclusions Conclusions Relative Levels Some Radionuclide Activity Relative Radionuclide Levels in in Selected Selected Media media monitored Some media Media monitored in Activity in the the TERRESTRIAL PATHWAY TERRESTRIAL PERCENT TOTAL PERCENT PATHWAY TOTAL environment are environment are significant significant for for the the GAMMA ACTIVITY GAMMA ACTIVITY numbers of numbers of gamma-emitting gamma-emitting radionuc1ides routinely radionuc1ides routinely measured measured at at SOIL levels exceeding levels exceeding analysis MDCs.
analysis MDCs.
Sediment Sediment in in the the aquatic aquatic pathway pathway and and soil soil in in the the terrestrial pathway are terrestrial pathway are two two such media.
such media.
The The following following graphs graphs show show the the relative relative activity activity contributions contributions for for the the types types ofof gamma-emitting radionuc1ides gamma-emitting radionuc1ides reported reported at levels at levels above above the the analysis analysis MDCs MDCs in in O.or.
sediment and sediment and soil soil at at indicator indicator locations locations during 2004.
during 2004.
AQUATIC PATHWAY AQUATIC PATHWAY Naturally occurring radionuc1ides Naturally occurring radionuc1ides PERCENT PERCENT TOTAL TOTAL accounted for accounted for 99.8 99.8 % of the gamma-
% ofthe gamma-GAMMA ACTIVITY GAMMA ACTIVITY emitting activity emitting activity in in both both sediment sediment and and soil in soil in 2004.
2004. Man-made Man-made radionuc1ides radionuc1ides of SSES of SSES origin origin accounted accounted for for 0.0%
0.0% ofof the gamma-emitting the gamma-emitting activity activity in in sediment sediment SEDIMENT during 2004.
during 2004. Man-made Man-made radionuclides radionuc1ides of non-SSES of non-SSES origin origin account account for for the the rest rest of the of the gamma-emitting gamma-emitting activity activity in in sediment and sediment and soil soil during during 20042004 ..
Generally, the Generally, the activity activity for for naturally naturally occurring radionuc1ides occurring radionuc1ides reported reported in in sediment and sediment and soil soil dwarfs dwarfs the the activity activity of of the man-made the man-made radionuc1ides.
radionuc1ides.
Manmade:
Manmade:
SSES SSES 0.0%
0.0%
44 2004 Radiological 2004 Radiological Environmental Environmental Monitoring Monitoring Report Report
Summan' and Summan' and Conclusions Conclusions Radionuclides Contributing to Dose from SSES Operation Of the three Of the three man-made man-made radionuclides radionuclides reported in reported in the the environment environment by by the the SSES REMP SSES REMP (i.e. (i.e. H-3, H-3, 1-131 1-131 andand Cs-Cs-137), tritium 137), tritium is is the the only only radionuclide radionuclide attributable to attributable to SSES SSES operation.
operation.
The whole body The whole body and and organ organ dosedose to to members of members of the the public public attributable attributable to to tritium identified tritium identified in in REMP REMP blowdown blowdown samples was samples was 0.0015 0.0015 mrem.
mrem.
Tritium Tritium was was included included in in the the dose dose calculation because calculation because it it was was identified identified inin the REMP the REMP samples samples of of water water being being discharged to discharged to the the river.
river. The The concentration of concentration of tritium tritium inin the the water water and and the volume the volume of of water water discharged discharged were were used to used to determine determine the the amount amount of of tritium tritium released. The released. The presumed presumed exposure exposure
."-./
."-./ pathways to pathways to the the public public from from this this radionuclide were radionuclide were drinking drinking water water taken taken from the from the Susquehanna Susquehanna River River at at Danville, P Danville, PA,A, and and eating eating fish fish caught caught near the near the SSES SSES discharge discharge to to the the river.
river.
This assumption This assumption is is based based on on the the fact fact that tritium that tritium doesdoes notnot emit emit gamma gamma radiation and radiation and thethe beta beta radiation radiation emitted emitted by tritium by tritium is is not not sufficiently sufficiently penetrating penetrating to reach to reach an an individual individual on on the the shore.
shore.
2004 Radiological 2004 Radiological Em'ironmental Em'ironmental Monitoring Monitoring Report Report 5 5
RadiologiCal RadiologiCal Environmental Environmental Key objectives of Key objectives of the the SSES SSES REMP REMP are are Monitoring Program Monitoring Program as follows:
as follows:
(REMP)
(REMP)
- Document compliance with Document compliance with SSES SSES The SSES is The SSES is located located on on an an REMP Technical REMP Technical Requirements Requirements approximately 1500-acre approximately 1500-acre tract tract along along the the radiological environmental radiological environmental Susquehanna River, Susquehanna River, five five miles miles northeast northeast surveillances surveillances of Berwick of Berwick in in Salem Salem Township, Township, Luzerne County, Luzerne County, Pennsylvania.
Pennsylvania. The: The: ** Verify proper implementation Verify proper implementation of of area around area around the the site site is is primarily primarily rural, rural, .. SSES radiological SSES radiological effluent effluent controls controls consisting predomiriately consisting predomiriately of forest and of forest and hinds..
agricultural hinds agricultural .. {More
{More specific specific ** Identify, measure, and Identify, measure, and evaluate evaluate information on information on the the demography, demography, trends of trends of radiomiclide radiomiclide
hydrology, meteorology, hydrology, meteorology, and and land land use use concentrations in concentrations in environmental environmental characteristics of characteristics of the the area area in in the the vicinity vicinity pathways near pathways SSES near SSES the SSES of the of SSES can can bebe found found in in the the
.. Environmentat'Report Environmentat'Report (Reference (Reference 1)" 1)" ** Assess impact Assess impact of of SSES SSES Effluents Effluents on on the Final the Final Safety Safety Analysis Analysis Report Report environment and the environment and the the public public (Reference 2),
(Reference 2), and'the and'the Final Final Environmental Statement Environmental Statement (Reference (Reference 3) 3) PPL PPL has has maintained maintained aa Radiological Radiological for the for the SSES.)
SSES.) Environmental Monitoring Environmental Monitoring Program Program
,, (REMP)
(REMP) in in the the vicinity vicinity ofof the the existing existing The SSES implements The SSES implements the the REMP REMP in in Susquehanna Steam Susquehanna Steam Electric Electric Station Station accordance with accordance with Technical Technical Units 1 Units 1 and and 2 2 since since April, April, 1972, 1972, prior prior toto Specifications, Technical Specifications, Technical Requirements Requirements construction of construction of both both units units and and ten ten years years Manual and Manual and thethe Offsite Offsite DoseDose prior to prior the initial to the initial operation operation of of Unit Unit 1 1 in in Calculation Manual, Calculation Manual, which which are are based based on on ~eptember, 1982. 1982. TheThe purpose purpose of of the the the design the design objeCtives objeCtives in in 10CFR 10CFR Part Part 50'50' preoperational REMP preoperational REMP (April, (April, 1972 1972 toto Appendix I, Appendix I, Sections Sections IV.B.2;IV.B.3,'
IV.B.2;IV.B.3,' September," 1982)
September," 1982) waswas toto establish establish aa and IV and IV .C.
.C. .~ baseline for baseline for radioactivity radioactivity in in the local the local The REMP The REMP supplements supplements the the results results of of enviroriment that enviroriment could be that could be compared compared the radioactive the radioactive effluent-monitoring effluent-monitoring with the with the radioactivity radioactivity levels levels observed observed in in program by program by verifying verifying that that the the various environmental various environmental media media measurable concentrations measurable concentrations of of .. throughout the throughout the operational operational lifetime lifetime of of radioactive materials radioactive materials and and levels levels of of the SSES.
the SSES. This This comparison comparison faciJitates faciJitates radiation in radiation in the the environment environment are are not not :,'>,
- ,'>, assessments of assessments of the the radiological radiological impact impact higher than higher than expected expected on on the the basis basis ofof the the of the of the SSES SSES operation.
operation.
effluent measurements effluent measurements and and modeling modeling of: of:
environment in the environment in the the vicinity vicinity of of the the SSES.
SSES.
2004 Radiological 2004 Radiological ED\'ironmental ED\'ironmental Monitoring Monitoring Report Report 6 6
Introduction Potential Exposure Pathways monitoring locations, called monitoring locations, called control control andand The three pathways The three pathways through through which which indicator locations, indicator locations, werewere established established to to radioactive material radioactive material may may reach reach thethe further assist further assist inin assessing assessing the the impact impact of of public from public from nuclear nuclear power power plants plants are are the the the station the station operation.
operation. Control1ocations Control1ocations atmospheric, terrestrial, atmospheric, terrestrial, and and aquatic aquatic are located are located at at sites sites where where it it is is pathways. (Figure pathways. (Figure 1 1 depicts depicts these these considered' unlikely considered' unlikely that that radiation radiation or or pathways for pathways for the the intake intake ofof radioactive radioactive radioactive material radioactive material fromfrom nonnal nonnal station station materials.)
materials.) operation would operation would be be detected.
detected. Indicator Indicator locations are locations are sited sited where where it it is is expected expected Mechanisms Mechanisms by by which which people people may may be be that radiation that radiation and and radioactive radioactive material material exposed to exposed to radioactivity radioactivity and and radiation radiation in in that might that might originate originate from from the the station station the environment the environment vary vary with with the the pathway.
pathway. would be would be most most readily readily detectable.
detectable.
Three mechanisms Three mechanisms by by which which aa member member of the of the public public has the potential has the potential to to be be Control locations for Control locations for the the atmospheric atmospheric exposed to exposed to radioactivity radioactivity or or radiation radiation and terrestrial and terrestrial pathways pathways are are more more thanthan from nuclear from nuclear power power plants plants such such as as the the 10 miles 10 miles from from the the station.
station. Preferably, Preferably, SSES are SSES are asas follows:
follows: the controls the controls alsoalso are are in in directions directions from from the station the station less less likely likely to to bebe exposed exposed to to wind blowing wind blowing from from thethe station station thanthan are are
- inhalation (breathing) inhalation (breathing) the indicator the indicator locations. Control_
locations. Control_
locations for locations for the the aquatic aquatic pathway, pathway, the the
- ingestion (eating ingestion (eating and and drinking),
drinking), andand Susquehanna River, Susquehanna River, areare upstream upstream of of the the station's discharge station's discharge to to the the river.
river.
- whole whole bodybody irradiation irradiation directly directly from aa plant from plant or or from from immersion immersion in in Indicator locations Indicator locations are are selected selected the radioactive the radioactive effluents.
effluents.
primarily primarily on on the the basis basis ofof proximity proximity to to the station, the station, although although factors factors such such as as REMPScope REMPScope meteorology, topography, meteorology, topography, and and sampling sampling The The scopescope of of the the SSES SSES REMPREMP was was practicality also practicality also areare considered.
considered.
developed based developed based on on the the NRC's NRC's Indicator locations Indicator locations for for the the atmospheric atmospheric Radiological Assessment Radiological Assessment Branch Branch and terrestrial and terrestrial pathways pathways are are typically typically Technical Position Technical Position on on radiological radiological less than less than 10 10 miles miles fromfrom thethe station.
station.
environmental monitoring, environmental monitoring, as as described described Most often, Most often, they they are are within within 5 5 miles miles of of in Revision in Revision 1, 1, November November 1979 1979 the station.
the station. Indicator Indicator locations locations in in the the (Reference 4).
(Reference 4). However, However, the the REMP REMP Susquehanna River Susquehanna River are are downstream downstream of of conducted by conducted by PPL PPL forfor the the SSES SSES exceeds exceeds the station's the station's discharge.
discharge. Monitoring Monitoring some of some of the the monitoring monitoring suggested suggested by by results from results from indicator indicator locations locations are are the NRC's the NRC's branch branch technical technical position, position, inin compared with compared with results results from from control control tenns of tenns of the the number number of of monitoring monitoring locations. These locations. These comparisons comparisons are are made made locations, the locations, the frequency frequency of of certain certain to discern to discern anyany differences differences in in the the levels levels monitoring. the monitoring. the types types ofof analyses analyses andlor types andlor types ofof radioactive radioactive material material required for required for the the samples, samples, andand the the and/or radiation and/or radiation that that might might exist exist achievable analysis achievable analysis sensitivities.
sensitivities. between indicators between indicators and and controls controls and and that that could be could be attributable attributable to to the the station.
station.
During During the the operational operational period period of of the the SSES, two SSES, two different different categories categories of of 77 2004 Radiological 2004 Radiological Environmental Environmental Monitoring Monitoring Report Report
Introduction Introduction In 2004 ,, the In 2004 the SSES SSES REMP REMP collected collected
.. II 850 850 identification of identification of SSES SSES radiation radiation and and samples at samples at 37 37 locations locations andand perfonned perfonned radioactive material difficult.
radioactive material difficult. Together, Together, 1,388 analyses.
1,388 analyses. In In addition, addition, the the REMP REMP this radiation this radiation and and radioactive radioactive material material monitors ambient monitors ambient radiation radiation levels levels using using present background present background levels levels from from which which thennoluminescent dosimeters thennoluminescent dosimeters (TLDs) (TLDs) an attempt an attempt isis made made to to distinguish distinguish at 58 at 58 indicator indicator and and control control locations, locations, relatively small relatively small contributions contributions from from thethe making as making as many many as as 253 253 radiation radiation level level SSES. This SSES. This effort effort is is further further measurements each measurements each year.
year. TheThe media media complicated by complicated by the the natural natural variations variations monitored and monitored and analyses analyses perfonned perfonned are are that typicaUy that typicaUy occur occur from from both both summarized in summarized in the the table table below:
below: monitoring location monitoring location to to location location andand with with Figures 22 through Figures through 77 display display the the REMP REMP time at time at the the same same locations.
locations.
1LDs and 1LDs and sampling sampling locations locations in in the the vicinity of vicinity of the the SSES.
SSES. Appendix Appendix C C The naturally occurring The naturally occurring radionuclides radionuclides provides directions, provides directions, distances, distances, and and aa potassium-40, beryllium-7, potassium-40, beryllium-7, radium-226, radium-226, brief description brief description of of each each ofof thethe locations locations thorium-228, and thorium-228, and tritium tritium are are routinely routinely in Figures in Figures 22 through through 7. 7. observed in observed in certain certain environmental environmental media. Potassium-40 media. Potassium-40 has has been been observed observed in a11 in a11 monitored monitored media media and and isis routinely routinely seen at seen at readily readily detectable detectable levels levels inin such such REMP Monitoring REMP Monitoring Sensitivity Sensitivity media as media as milk, milk, fish, fish, fruits fruits and* --
vegetables.
vegetables. Seasonal Seasonal variations variations in in beryllium-7 beryllium-7 in air samples in air samples are are regularly' regularly' Detection Detection of of radiation radiation and and radioactive radioactive observed. Man-made observed. Man-made radionuclides, radionuclides, material from material from thethe SSES SSES in in the the such as such as cesium-137 cesium-137 left left over over from from environment is environment is complicated complicated by by the the nuclear weapons nuclear weapons testing testing are are often often presence of presence of naturally naturally occurring occurring radiation radiation observed as observed as well.
well. InIn addition, addition, thethe and radioactive and radioactive materials materials from from both both radionuclide tritium, radionuclide tritium, produced produced by by both both terrestrial and terrestrial and cosmic cosmic sources.
sources. Man- Man- cosmic radiation cosmic radiation interactions interactions in in the the made radiation made radiation and and radioactive radioactive materialmaterial upper atmosphere upper atmosphere as as well well as as man~made from non-SSES from non-SSES sources, sources, such such as as nuclear nuclear (nuclear weapons),
(nuclear weapons), is is another another fallout from fallout from previous previous nuclear nuclear weapons weapons radionuclide typically radionuclide typically observed.
observed.
tests and tests and medical medical wastes, wastes, also also can can make make SSESREMP SSESREMP TYjlc of Monitoring TYjlc of Monitoring Media Monitored Media Monitored Gross Alpha Gross Alpha Activity Activity Drinking Water Drinking Water Gross Beta Gross Beta Activity Activity All Waters, All Waters, except except Ground Ground Water, Water, and and Air Air Particulates Particulates RadionucIide Activities Gamma-Emittin~ RadionucIide Activities All Media All Media Tritium Activity Tritium Activity All Waters All Waters Jodine-131 Activity Jodine-131 Activity Surface Water.
Surface Water. Drinking Drinking Water.
Water. Air Air && Milk Milk Exposure Rates Exposure Rates Ambient Radiation Ambient Radiation Levels Levels (by TI.D)
(by TI.D) 2004 Radiological 2004 Radiological Em'ironmental Em'ironmental Monitoring Monitoring Report Report 8 8
II Introduction Radioactivity levels in Radioactivity levels in environmental environmental media are media are usually usually so low that so low that their their measurements, even measurements, even withwith state-of-the-state-of-the-measurement methods, art measurement art methods, typically typically have significant have significant degrees degrees of of uncertainty uncertainty associated with associated with lhem.(Reference lhem.(Reference 5) As
- 5) As aa result, result, expressions expressions are are often often used used when referring when referring toto these these measurements measurements that convey that convey information information aboutabout thethe levels levels being measured being measured relative relative toto the the measurement sensitivities.
measurement sensitivities. TermsTerms such such as "minimum as "minimum detectable detectable concentration" concentration" (MDC) are (MDC) are used used for for this this purpose.
purpose. TheThe formulas used formulas used toto calculate calculate MDCs MDCs may may be found be found inin procedures procedures referenced referenced in in Appendix A.
Appendix A.
The methods of The methods of measurement measurement for for sample radioactivity sample radioactivity levels levels used used byby PPL's contracted PPL's contracted REMP REMP radioanalytical radioanalytical laboratories are laboratories are capable capable of of meeting meeting the the analysis sensitivity analysis sensitivity requirements found requirements found in the in the SSES SSES Technical Technical Requirements.
Requirements.
9 9 2004 Radiological 2004 Radiological Environmental Environmental Monitoring Monitoring Report Report
11~--"
Exposure PaJ,~war-s.\ to..-IJum~ns Exposure
,,:: ",", p:J":;-(j,:<n<-
p:J":;-(j,:<n<- "'\-:! ";
"'\-:! "; " " "
"",,*\:,,-*;:/,~ :*,:c:c~;:;,',:;::~:.'*6as~olls*:Emueni<,'>~.' ,,::,,
.. ~
~. '.
,'. ~ -- "" .. ~ -- .'
.. ~ .... -- .
'\
'\ Uquid Uquid
~ EfDuent EfDuent Direct Direct Irradiation Irradiation Figure 1 Figure 1
FIGURE 2 FIGURE 2 2004 TLD MONITORING LOCATIONS WITHIN ONE MILE OF THE SSES Co?;7 Co?7
- 2004 TLD 2004 FROM ONE FROM ONE TO FIGURE TO FIVE 3
FIGURE 3 TLD MONITORING MONITORING LOCATIONS FIVE MILES LOCATIONS MILES FROM FROM THE THE SSES SSES
FIGURE 4 FIGURE 4 2004 2004 TLD TLD MONITORING MONITORING LOCATIONS LOCATIONS GREATER GREATER THAN THAN FIVE FIVE MILES MILES FROM FROM THE THE SSES SSES
FIGURE FIGURE 5 5 2004 ENVIRONMENTAL 2004 ENVIRONMENTAL SAMPLING SAMPLING LOCATIONS LOCATIONS WITHIN ONE WITHIN ONE MILE MILE OF OF THE THE SSES SSES 1 MILE CO(y
- Q 2004 FROM ONE ONE TO
,.t FIGURE FIGURE 6 2004 ENVIRONMENTAL ENVIRONMENTAL SAMPLING FROM FIVE MILES TO FIVE MILES FROM 6
SAMPLING LOCATIONS LOCATIONS FROM THE SSES THE SSES
( lake Fltneerest Oem
~ ,; - - - --
U * ;/ .
ff
- .. " Sticksti Mc<xrta.,rTf'I
- ~,.,
C07 C07
FIGURE 7 FIGURE 7 2004 ENVIRONMENTAL SAMPLING 2004 ENVIRONMENTAL SAMPLING LOCATIONS LOCATIONS GREATER GREATER THAN THAN FIVE FIVE MILES MILES FROM FROM THE THE SSES SSES
Ambient Radiation Ambient Radiation Monitoring Monitoring AMBIENT RADIATION AMBIENT RADIATION MONITORING MONITORING INTRODUCTION INTRODUCTION due due toto locational locational differences differences in in such such The primary method The primary method for for the the SSES SSES factors as factors as soil soil characteristics characteristics (amounts (amounts REMP's measurement REMP's measurement of of ambient ambient of organic of organic matter, matter, partic1e'size, partic1e'size, etc.),
etc.),
radiation levels radiation levels is is the the use use of of drainage opportunities, drainage opportunities, and and exposure exposure to to thermoluminescent dosimeters thermoluminescent (TLDs).
dosimeters (TLDs). sunlight. Environmental sunlight. Environmental TLDs TLDs can can also also The TLDs The TLDs are are crystals crystals (calcium (calcium sulfate) sulfate) be affected be affected by by direct direct radiation radiation (shine)
(shine) ,,
capable of capable of detecting detecting and and measuring measuring low low from the from the SSES SSES turbine turbine buildings buildings during' during' levels of levels of radiation radiation by by absorbing absorbing aa operation, radwas!e operation, radwas!e transfer transfer and and storage, storage, portion of portion of the the radiation's radiation's energy energy that that isis and radioactive and radioactive gaseous gaseous effiuents effiuents from from incident upon incident upon them them andand storing storing the the the SSES.
the SSES.
captured energy captured energy until until the the TLDs TLDs are are processed (read).
processed (read). Processing Processing involves involves .. Unfortunately, Unfortunately, TLDs TLDs do do not not have have any any heating the heating the TLDs TLDs to to release release their their stored stored inherent ability inherent ability to to indicate indicate thethe source source ofof energy in energy in the the form oflight and form oflight and the radiation the radiation to to which which theythey are are exposed.
exposed.
measuring the measuring the intensity intensity of of the the light light that that The placement The placement of of numerous numerous TLDs TLDs in in they emit.
they emit. The The intensity intensity of of the the emitted emitted the environment the environment can can facilitate facilitate decision'-
decision'-
light is light is proportional proportional to to the the amount amount of of making about making about the the possible possible radiation radiation radiation to radiation to which which they they were were exposed.
exposed. sources to sources to which which TLDs TLDs are are exposed.
exposed.
Calibration of Calibration of the the TLD TLD processors processors However, aa method However, method for for evaluating evaluating TLD TLD
,, permits permits aa reliable reliable relationship relationship to to be be data is data is still still required. 'The SSES required. 'The SSES REMPREMP established between established between the the light light emitted emitted relies on relies on aa statist!cally statist!cally based based approach approach and the and the amount amount of of radiation radiation dosedose to simultaneously to simultaneously compare compare indicator indicator received by received by thethe TLDs.
TLDs. The The result result ,, TLD data TLD data with with control control TLD TLD data and data and permits accurate permits accurate measurements measurements of of the the operational TLD operational TLD data data with with ambient radiation ambient radiation in in the the environment.
environment. preoperational TLD preoperational TLD data.
data. This This approach permits approach permits thethe flagging flagging of of Environmental TLDs Environmental TLDs are are continually continually "" environmental TLD environmental TLD doses doses that that might' might' exposed exposed to to natural natural radiation radiation from from the,""
the,"" have been have been produced produced by by both both man-made' man-made' ground (terrestrial ground (terrestrial radiation) radiation) and and from from sources of sources of radiation, radiation, as as well well asas natural natural the sky the sky (cosmic)
(cosmic) radiation.
radiation. In In addition, addition, radiation sources.
radiation sources. It It also also provides provides aa they also they also may may be be exposed exposed 'to 'to man-made',
man-made', means for means for attributing attributing aa portion portion of of the the radiation. Most radiation. Most of of the the environmentai environmentai total TLD total TLD dosedose toto SSES SSES operation operation if if TLD's natural TLD's natural radiation radiation exposure exposure comes comes appropriate.
appropriate.
from sources from sources in in ~he'grou~d. 'Th~se ,, ""
terrestrial sources terrestrial sources varyvary naturally naturally with with "" Interpretation Interpretation of of environmental environmental TLD TLD time due time due to to changes changes in in soii soii moisture'"
moisture'" :: results is results is described described in in PPL PPL Nuclear Nuclear snow cover,'
snow cover,' etc.etc. The' The' natural-radiation' natural-radiation' Engineering Study, Engineering Study, EC-ENVR-1012 EC-ENVR-1012 picture is picture is complicated complicated becausebecause the the ,,', ,,', (Revision 0, (Revision 0, January January 1995).
1995).
factors affecting factors affecting radiation radiation reaching reaching the the ..
TLDs from TLDs from the the ground ground varyvary differently differently with time with time from from one one location location to to another another 2004 En\'ironmental 2004 En\'ironmental Radiological Radiological Monitoring Monitoring Report Report 17 17
Ambient Radiation Monitoring Scope Scope Direct made radiation measurements Direct radiation made using using Panasonic Panasonic UD-814 Panasonic measurements were Panasonic 71 UD-814 (calcium 71 OA were OA readers readers and (calcium sulfate) sulfate) and Monitoring Results Monitoring TLDs Results **
The TLDs The TLDs were were exchanged exchanged quarterly quarterly thermo luminescent thermo luminescent dosimeters dosimeters (TLD).(TLD).
and processed by and processed by thethe SSES SSES Health Health During 2004, During 2004, the the SSES SSES REMP REMP had had 4848 Physics Physics Dosimetry Dosimetry Group. Group. Average Average indicator, 55 control indicator, control and and 55 special special ambient gamma ambient radiation levels gamma radiation levels interest TLD interest TLD locations.
locations. Refer Refer to to Table Table measured measured by by environmental environmental TLDs TLDs C 11 and C and C2C2 for for TLD TLD measurement measurement generally generally remained remained constant constant throughout throughout locations. The locations. The TLDTLD locations locations are are placed placed 2004, as 2004, as shown shown in in the the bar bar graph graph below.
below.
on and on and around around the SSES site the SSES site as as follows:
follows:
A site boundary A site boundary ring ring (i.e. an inner (i.e. an inner ring) ring) 2004 2004 consisting of consisting of 1818 locations locations (1 (1 S2, S2, 2S3 2S3 ,, REMP Quarterly REMP Quarterly TLD TLD Averages Averages 25.0 ,
25.0 ,- ---------:, -- ---- -- ---- ------- ---- -,,
3S2, 4S3 3S2, 4S3 ,, 5S7, 5S7, 6S4, 6S4, 6S9, 6S9, 7S6, 7S6, 8S2, 8S2, 9S2, 10S2, 9S2, 10S2, 11S3, 11S3, 12S3, 12S3, 13S2, 13S2, 13S5, 13S5, ..: 20.0
..: 20.0 15S5, 16S1 15S5, 16S1 andand 16S2) 16S2) nearnear and and within within ~
'C
'C 15.0 15.0 Wi 10.0 Wi ii?
the site the site perimeter perimeter representing representing fence fence ii? 10.0 post doses post doses from from aa SSES SSES release.
release. E E 5.0 5.0 0.0 0.0 An outer distance An outer distance ringring consisting consisting of of 30 30 22 33 44 locations (ID5 locations (ID5 ,, 2S2, 2S2, 2F12F1 ,, 3S3 3S3 ,, 3E1 3E1 ,, Calendar Quarters Calendar Quarters ** Indicator Indicator
- Control Control 4S6, 4E2, 4S6, 4E2, 5S4, 5E2,6E1 ,, 7S7, 5S4, 5E2,6E1 7S7, 7E17E1 ,,
8A3 ,, 8D3 8A3 8D3 ,, 9B1 9B1 ,, 9D4, 9D4, lOS1, lOSl, lOD1 lOD1 ,,
- 11S7, 11S7, 11E111E1 ,, 12S1, 12S1, 12S7, 12S7, 12D2, 12D2, 12E112E1 ,, Indicator environmental TLD Indicator environmental TLD results results for for
- 13S6, 13S6, 13E4, 13E4, 14S5, 14S5, 14D1, 14D1, 15F115F1 and and 2004 were 2004 were examined examined quarterly quarterly on on an an 16F1) extending 16F1) extending approximately approximately 55 miles miles individual location individual location basis basis and and compared compared from from SSES.
SSES. These These TLD'TLD' ss areare designed designed with both with both current current control control location location to to measure measure possible possible exposures exposures to to c1ose-c1ose- results and results and preoperational preoperational data. data. VeryVery in in population.
population. small SSES small SSES exposure exposure contributions contributions were identified were identified during during 20042004 at at twelve twelve The balance of ten locations represent onsite locations as onsite locations follows :: 11S2, as follows S2, 6S4, 6S4, the control the control andand special special interest interest areas areas 6S9, 6S9, 7S6,7S6, 9S2, 9S2, 10S2, 10S2, 11S3, 11S3, 12S312S3 ,, 12S4, 12S4, such as such as population population centers, centers, schools, schools, etc.etc. 13S2, 13S2, 13S5,13S5, and 16S2.
and 16S2.
The five The five control control locations locations are are 3G4, 3G4, 4G 4G 1, 1,
7G1 , 12G1 7G1, 12G1 andand 12G4.
12G4. The The five five special special The The highest, highest, estimated, estimated, gammagamma interest locations interest locations are are 6A4, 6A4, 15A3, 15A3, 16A2,16A2, radiation dose radiation dose ofof 3.88E-02 3.88E-02 rnrem rnrem for for all all 8B2 and 8B2 OB3.
and 11OB3. of 2004 of 2004 was was atat location location 9S2.9S2. This This dose dose is approximately is approximately 0.16% 0.16% of of the the 25 25 rnrem rnrem The specific The specific locations locations were determined were determined whole-body SSES whole-body SSES Technical Technical according to to the the criteria criteria presented presented in in the the Requirements (TRO (TRO 3.11.3) 3.11.3) limit limit for for all all according Requirements NRC Branch NRC Branch Technical Technical Position Position on on SSES sources SSES sources of of radioactivity radioactivity and and Radiological Radiological Monitoring Monitoring (Revision (Revision 1, 1, radiation.
radiation.
November 1979).
November 1979).
18 18 2004 Environmental 2004 Environmental Radiological Radiological Monitoring Monitoring ReportReport C03A CO?;A
Ambient Radiation Ambient Radiation Monitoring Monitoring Refer Refer to to the the following following forfor results results ofof TLD measurements TLD measurements for for 2004:
2004:
- Figure Figure 8,8, trends trends quarterly quarterly TLD TLD results for results for both both preoperational preoperational and and operational periods operational periods
- Appendix Appendix G, G, Table Table G G Summary Summary of of Data Table, Data Table, page page 11 of of 13 13 shows shows thethe averages for averages for TLD TLD indicator indicator andand control locations control locations for for the the entire entire year.
year.
- Appendix Appendix H, H, Table Table HI, HI, page page H-3 H-3 shows aa comparison shows comparison of of the the 2004 2004 mean indicator mean indicator and and control control TLDTLD results with results with the the means means for for the the preoperational and preoperational and operational operational periods at periods at the the SSES.
SSES.
- Appendix I, Appendix I, Table Table 1-1, 1-1, page page 1-2 1-2 shows shows TLDTLD results results for for all all locations locations for each for each quarter quarter ofof 2004.
2004.
2004 Environmental 2004 Environmental Radiological Radiological Monitoring Monitoring Report Report 19 19
FIGURE 8 FIGURE 8 -- AMBIENT AMBIENT RADIATION RADIATION LEVELS LEVELS Exposure Rate Exposure Rate (mRlSTD (mRJSTD Qtr)
Qtr) BASED ON BASED ON TLD TLD DATA DATA 50 ~----------------------~---------------------------------------------------.
~----------------------~----------------------------------------------------~
PRE OPERA PRE OPERA TIONAL TIONAL OPERATIONAL OPERATIONAL 45 45 40 40 35 35 Unit2 Unit2 30 30 Criticality Criticality 25 25 20 20
//
15 15 10 10 55 O +-~~~--~~~~~--~~~~~~~~~~~~~~~~~~--~~~~~~~~~
+-~~~--~~~~--~~~~--~~~~~~~~~~--~~~~--~~~~--~~~~
~
(\",
(\",
~
(\~
~
(\"(\"
-- Indicator Indicator -- Control Control
Aquatic Pathway Aquatic Pathway Monitoring Monitoring INTRODUCTION INTRODUCTION low.:.level radioactive discharges low.:.level radioactive discharges enterenter In 2004 the In 2004 the SSES SSES REMPREMP monitored monitored the the the river.
the river. TheThe upstream upstream monitoring monitoring following media following media in in the the aquatic aquatic pathway:
pathway: locations serve locations serve asas controls controls to to provide provide surface water, surface water, drinking drinking water, water, fish, and' fish, and' data for data for companson companson with with downstream downstream sediment;< Some sediment;< Some of of the the media media (e.g.,(e.g., <<< <<< monitoring results.
monitoring The potential results. The potential exists exists drinking 'water drinking 'water andand fish) fish) provide provide for radioactive for radioactive material material thatthat might might be be information that information that can can bebe especially especially usefuluseful present in present in SSES SSES airborne airborne releases releases to to to the to the estimation estimation of of possible possible dosedose to to the the enter the enter the Susquehanna Susquehanna River River upstream upstream public from public from potentially potentially ingested ingested <
< of the of the plant plant through through either either direct direct radioactivity, if radioactivity, if detected.
detected. OtherOther media, media, deposition (e.g.,
deposition (e.g., settling settling or or washout) washout) or or such as such as sediment, sediment, can can bebe useful useful for.for. ,.,. by way by way ofof ~noff fromfrom deposition deposition on on trending radioactivity trending radioactivity levelslevels in in thethe .. <
< land adjacent land adjacent to to the the river.
river. However, However, aquatic pathway, aquatic pathway, primarily primarily ,because
,because of of direct deposition direct deposition and and runoff runoff areare their tendency their tendency to to assimilate assimilate certain certain considered to considered to be be irisignificant irisignificant as as means means materials that materials that might might enter enter the the surface surface of entry of entry for for SSES SSES radioactivity radioactivity intointo the the water to water to which which they are exposed.
they are exposed. The The Susquehanna River Susquehanna River when when compared compared to to results from results from monitoring monitoring all all of of these these !iquid discharges
!iquid discharges underunder normal normal media provide media provide aa picture picture of of the the aquatic aquatic conditions.
conditions.
pathway that pathway that is is clearer clearer than than that that which which < <
could be could be obtained obtained if if one one or or more more werewere Lake Took-a-'Vhile (LTAW),
Lake Took-a-'Vhile (LTAW), which which is is not included not included in REMP.
the REMP.
in the located in located PPL's Riverlands in PPL's Riverlands Recreation Recreation Area adjacent Area adjacent to to the the Susquehanna Susquehanna Fruits Fruits oror vegetables vegetables that that are are grown grown in in River. is River. is also also considered considered to be part to be part of of fields inigated fields inigated with with surface surface water water would would the aquatic the aquatic pathway pathway for for monitoring monitoring be, in also be, also in the the aquatic pathway. The aquatic pathway. The .. purposes. Although purposes. Although it it is not in is not in aa land use land use census census (Reference (Reference 11) 11) :::: position to position to receive receive water water discharged discharged to to conducted in conducted in 2004 2004 looked looked at at farms farms the river the river from from the the SSES.
SSES. it it can can receive receive
\vithin 10
\vithin 10 miles miles downstream downstream the ofof the .. storm runoff storm runoff from runoff from runoff from the from the the SSES the SSES.
SSES site SSES. Storm Storm site should should notnot SSES. The SSES. The Lupini Lupini FarmFarm in in Mifflinville Mifflinville < <
(12F7) briefly (12F7) briefly inigated inigated potatoes potatoes in in June June contain< any normally contain<
normally any measurable measurable 2004 using 2004 using Susquehanna Susquehanna River River water.'
water.' radioactivity from radioactivity from thethe plant.
plant. However, However, No other No other fields fields within within 10 10 miles miles ..
.. the SSES the SSES REMP, REMP, consistent consistent withwith other other downriver of downriver of Susquehanna Susquehanna SES SES were were aspects of aspects of aquatic aquatic monitoring monitoring and and thethe inigated in inigated in 2004.
2004. REMP, in REMP, in general, general, goes beyond its goes beyond its requirements by requirements by monitoring monitoring LtAW.LtAW. < <
The aquatic pathway The aquatic pathway in in the the vicinity vicinity of of the SSES the SSES is is the the Susquehanna Susquehanna River. River.
Monitoring of Monitoring of all all of.
of. the the aquatic aquatic media,media, ..
except drinking except drinking water, water, is is conducted conducted -'. -'.
both downstream both downstream and and upstream upstream of of the) the) ..
location from location from whichwhich occasiona1 occasiona1 SSES SSES ..
2000 Radiological 2000 Radiological Environmental Environmental Monitoring Monitoring Report Report 21 21
j' j '
Aquatic Pathway Aquatic Pathway Monitoring Monitoring Scope Scope receiving runoff receiving runoff from from thethe SSES.
SSES.
LTAW LTAW is is considered considered an an indicator indicator location.
location.
Surface Water Surface water was Surface water was routinely routinely sampled sampled from the from the Susquehanna Susquehanna River River at at one one Sedimellt indicator location indicator location (6S5) (6S5) andand oneone control control Sediment sampling was Sediment sampling was performed performed in in location (6S6) at location (6S6) at the the SSESRiver SSESRiver Water' Water' the spring the spring andand fall fall at at indicator indicator locations locations Intake during Intake during 2004.2004. Sampling Sampling also also took took 7B and 7B and 12F 12F andand control control location location 2B2B onon place at place at the the following following additional additional the Susquehanna the Susquehanna River. River. In In addition, addition, indicator locations:
indicator locations: ~he SSES SSES discharge discharge sediment was sediment was also also obtained obtained from from line to line to the the river (2S7/6S7) and river (2S7/6S7) and Lake Lake location LTAW.
location LTAW.
Took-A-While (LTAW).
Took-A-While (LTAW).
Sampling Sampling Drillkillg Water Drillkillg Water Drinking water samples Drinking water samples were were collected collected Surface Water Surface Water at location at location 12H2, 12H2, the the Danville Danville Weekly water samples Weekly water samples werewere collected collected Municipal Water Municipal Water Authority's Authority's treatment treatment at indicator at indicator location location 6S56S5 for for both both facility on facility on the the Susquehanna Susquehanna River, River, in in biweekly and biweekly and monthly monthly compositing.
compositing.
2004. Treated 2004. Treated waterwater is is conected conected from from Location 6S5 Location 6S5 waswas considered considered aa backup backup the end the end of of the the processing processing flowpath, flowpath, for locations for locations 2S7 2S7 and and 6S7 6S7 inin the theevent event representing finished representing finished water water thatthat isis that water that water could could notnot be be obtained obtained from from suitable for suitable for drinking.
drinking. This This is is the the nearest nearest the automatic the automatic samplers samplers at at these these point downstream point downstream of of the the SSES SSES locations. Routine locations. Routine samples samples for for 6S5 6S5 discharge to discharge to the the River River at at which which drinking drinking were collected were collected from from aa boat, boat, unless unless ri ri ver ver water is water is obtained.
obtained. No No drinking drinking waterwater conditions prohibited conditions prohibited boating.
boating. When When control location control location is is sampled.
sampled. For For allall this occurs, this occurs, samples samples are are collected collected from from intents and intents and purposes, purposes, control control surface surface an alternate an alternate shoreline shoreline sitesite lOCated lOCated below below water sampling water sampling locations locations wouldwould be be the Susquehanna the Susquehanna SES SES discharge discharge suitable for suitable for comparison.
comparison. diffuser. The diffuser. The shoreline shoreline samples samples areare collected at collected at the the Wetlands Wetlands Cottage Cottage area, area, Fish Fish approximately 100-150 approximately 100-150 yards yards down down Fish were sampled Fish were sampled from from thethe river from river from thethe 6S5 6S5 site.
site.
Susquehanna River Susquehanna River in in the the spring spring and and of 2004, fall of fall 2004, at at one one indicator indicator location, location, Indicator locations 2S7 Indicator locations 2S7 and and 6S7, 6S7, the the IND, downstream IND, downstream of of the the SSES liquid SSES liquid SSES Cooling SSES Cooling TowerTower Blowdown Blowdown discharge to discharge to the the River River and and one one control control Discharge (CTBD)
Discharge (CTBD) line,line, and and control control location, 2H, location, 2H, sufficiently sufficiently upstream upstream to to location 6S6, location 6S6, thethe SSES SSES River River Water Water essentially preclude essentially preclude the the likelihood likelihood that that Intake structure, Intake structure, werewere time time --
fish caught fish caught there there would would spendspend any any time time proportionally sampled proportionally sampled using using automatic automatic below the below the SSES SSES discharge.
discharge. In In addition, addition, continuous samplers.
continuous samplers. The The samplers samplers fish were fish were also also sampled sampled in in the the fall fall from from were typicaIly were typicaIly setset to to obtain obtain 30-60 30-60 ml ml PPL's Lake PPL's Lake Took-a-While, Took-a-While, location location aliquots every aliquots every 20-25 20-25 minutes.
minutes. Weekly, Weekly, LTA\V.
LTA \V. This This location location is is not not the water the water obtained obtained by by these these samplers samplers downstream of downstream of the the SSES SSES discharge.
discharge. It It was retrieved was retrieved forfor both both biweekly biweekly andand is sampled is sampled because because of of its its potential potential for for monthly compositing.
monthly compositing.
2004 Radiological 2004 Radiological Environmental Environmental Monitoring Monitoring Report Report 22 22
Aquatic Pathway Monitoring Sediment and Fish The other surface The other surface water water monitoring monitoring Fish 'are frozen Fish 'are frozen until until shipment.
shipment. All All
location, LTAW, location, LTAW, was was grab grab sampled sampled samples are samples are a~alyzed by by gamma gamma once each once each month.
month. spectroscopy for spectroscopy for the the activities activities of of any any gamma emitting gamma emitting radionuclides radionuclides that that may' may' Drinking Water ,, .. be present.
be present.
Treated water was Treated water was time-proportionally time-proportionally sampled by sampled by an an automatic automatic sampler.
sampler. The The ,, Monitoring Results Monitoring Results sampler was sampler was typically typically setset to to obtain obtain three three 12-ml aIiquots 12-ml aIiquots every every twenty twenty minutes.
minutes. Surface Water Week1y, the Week1y, the water water obtained obtained by by th,is th,is Refer to the Refer to the fonowing fonowing for for results results of of sampler was sampler was retrieved retrieved for for both both biweekly biweekly surface water surface water analyses analyses for for 2004:
2004:
and monthly and monthly compo compo siting.
siting.
- Figure Figure 9 9 trends trends gross gross beta beta activities activities Fish Fish separately for separately for surface surface water water Fish were obtained Fish were obtained by by electrofishing.
electrofishing. indicator and indicator and control control locations locations Electrofishing stuns Electrofishing stuns thethe fish fish andand allows, allows, quarterly from quarterly from 1975 1975 through through 2004.2004.
them to them to float float to to the the surface surface so so that that those those of the of the desired desired species species and and sufficient sufficient sizesize ** Appendix G, Appendix G, Table Table G G page page l-and l-and 2 2 can be can be sampled.
sampled. Sampled Sampled fish fish include include of 13 shows of 13 shows aa summary summary of of the the 2004 2004 recreation ally recreation ally important important species, species, such such as as surface water surface water data.
data.
smallmouth bass, smallmouth bass, and and also also channel channel catfish and catfish and shorthead shorthead redhorse.
redhorse. The The ** Appendix Appendix H, H, Tables Tables H H 22 through through fish are fish are filleted filleted and and the the edible edible portions portions H 44 shows H shows comparisons comparisons of of gross gross are kept are for analysis.
kept for analysis. beta, iodine-131 beta, iodine-131 and and tritium tritium monitoring results monitoring results against against past past years years Sediment Sediment data.
data.
Shoreline sediment Shoreline sediment was was collected collected to to depths depths of of four four feet feet of of water.
water. ** Appendix Appendix I, I, Tables Tables 1-21-2 and and 1-3 1-3 shows specific shows specific results results ofof gross gross beta, beta, ,,
Sample Preservation Sample Preservation tritium, gamma tritium, gamma spectroscopic spectroscopic and and and Analysis and Analysis iodine-131 analyses iodine-131 analyses of of surface surface water water samples.
samples.
SlIrface and Drinking Water The Nuclear Regulatory The Nuclear Regulatory Commission Commission Surface Surface and and drinking drinking water water samples./,
samples./,
(NRC) requires (NRC) requires thatthat averages averages of of the the were analyzed were analyzed monthly monthly for for beta, beta, ..
activity levels activity for indicator levels for indicator gamma-emitting radionuclides, gamma-emitting radionuclides, and and environmental ,monitoring environmental ,monitoring locations locations and and tritium activities.
tritium activities. Biweekly Biweekly composite composite for control for control environmental environmental monitoring monitoring samples were samples were analyzed analyzed for for 1-131, 1-131, locations of locations of surface surface water, water, as well as as well as ..
activity. In activity. In addition, addition, drinking drinking waterwater """" ,,
other monitored other monitored media, media, bebe reported reported to to samples were samples were analyzed analyzed for for gross alpha. ""
gross alpha.
the NRC the NRC annually.
annually. Data Data from from thethe activity.
activity.
following three following three surface surface water water monitoring locations monitoring locations werewere averaged averaged 23 23 .. 2004 2004 Radiological Radiological Em'ironmcntal Em'ironmcntal Monitoring Monitoring Report Report
l' l'
Aquatic Pathway Monitoring together together as as indicators indicators for for reporting reporting water water in in the the crBD crBD is is maintained maintained at at aa purposes: one purposes: one location (6S5) on location (6S5) on the the flow rate flow rate of 5,000 gpm of 5,000 gpm or or higher.
higher. TheseThese Susquehanna River Susquehanna River downstream downstream of of the the requirements are requirements are in in place place to to ensure ensure SSES, Lake-Took-a SSES, Lake-Took-a While While (LTA (LTAW) W) adequate dilution adequate dilution ofof radioactively radioactively adjacent to adjacent to the the river, river, and and the the SSES SSES contaminated water contaminated water byby the the returning returning cooling tower cooling tower bIowdown bIowdown discharge discharge noncontaminated water noncontaminated water in in the the CTBn CTBn (crBD) line (crBD) line to to the the river river (2S7).
(2S7). prior to prior to entering entering thethe river.
river.
Technically, Technically, the the CTBD CTBD line line isis not not part part At the point At the point that that crBn crBn water water entersenters thethe of the of the environment.
environment. The The CTBD CTBD line line is is aa river, additional, river, additional, rapid rapid dilution dilution of of the the below ground below ground pipe pipe toto which which the the public public discharged water discharged water by by the the river river is is has no has no access, access, contrary contrary to to the the other other promoted by promoted by releasing releasing it it through through aa environmental monitoring environmental monitoring locations locations on on diffuser. The diffuser. The diffuser diffuser is is aa large large pipepipe the Susquehanna the Susquehanna River River toto which which the the with numerous with numerous holes holes inin it it that that is is public does public does have have access.
access. However, However, positioned near positioned near the the bottom bottom of of the the river.
river.
currently there currently there is is no no automatic automatic CTBD discharges CTBD discharges exitexit the the diffuser diffuser composite sampling composite sampling of of an an indicator indicator through the through the many many holes, holes, enhancing enhancing the the location on location on the the Susquehanna Susquehanna River, River, soso mixing of mixing of the the discharge discharge and and river river the CTBD the CTBD line line from from the the SSES SSES is is waters. The waters. The concentrations concentrations of of included as included as anan indicator indicator monitoring monitoring contaminants are contaminants are reduced reduced significantly significantly location in location in thethe radiological radiological as the as the discharged discharged waterwater mixes mixes with with thethe ..
environmental monitoring environmental monitoring program.
program. much larger much larger flow flow of of river river water.
water. The The mean flow mean flow rate rate of of the the Susquehanna Susquehanna Most Most of of the the water water entering entering the the River in River in 2004 2004 waswas approximately approximately Susquehanna River Susquehanna River through through the SSES the SSES 9,150,000 gpm.
9,150,000 gpm. This This isis more more than than CTBD line CTBD line is is simply simply water water thatthat was was 1,800 times 1,800 times the 5,000 gpm; the 5,000 gpm; required required taken from taken from the the river river upstream upstream of of the the minimum flow minimum flow rate rate through through the the crBD crBD SSES, used SSES, used for for cooling cooling purposes purposes for discharges for discharges to to be be permitted.
permitted. The The without being without being radioactively radioactively crBD average crBD average flow flow during during 2004 2004 was was contaminated by contaminated by SSES SSES operation, operation, and and 8,818 gpm.
8,818 gpm. BasedBased onon the the average average river river returned to returned to the the river.
river. Batch Batch discharges discharges flow and flow and thethe average average crBD crBD flow flow during during of relatively of relatively smallsmall volumes volumes of of slightly slightly 2004, Jiquid 2004, Jiquid discharges discharges fromfrom the the SSES SSES radioactively contaminated radioactively contaminated water water areare where diluted where diluted by by approximately approximately aa factor factor made to made to the the river river through through thethe SSES SSES 1,000.
of 1,000.
of CTBD at CTBD at times times throughout throughout each each year.
year.
The water The water is is released released fromfrom tanks tanks of of The amounts of The amounts of radioactively radioactively radioactively contaminated radioactively contaminated water water on on site site contaminated water contaminated water being being discharged discharged to the to the CTBD CTBD and and mixes mixes with with thethe are small.
are small. Nevertheless, Nevertheless, sensitive sensitive noncontaminated water noncontaminated water already already present present analyses of analyses of the the water water samples samples can can often often in the in the CTBD.
CTBD. Flow Flow rates rates from from the the tanks tanks detect the detect the low low levels levels of of certain certain typestypes of of containing radioactively containing radioactively contaminated contaminated radioactivity in radioactivity in the the CTBD CTBD water water water being water being discharged discharged to to the the crBD crBD following dilution.
following dilution. Though Though the the levels levels vary based vary based on on the the radioactivity radioactivity 1evel 1evel of of of radioactivity of radioactivity measured measured in in the the CTBD CTBD the batch the batch release.
release. ,In ,In addition, addition, the the water are water are generally generally quite quite low, low, theythey tend tend minimum flow minimum flow raterate for for the the returning returning to be to be higher higher thanthan those those in in the the river river 2004 Radiological 2004 Radiological Environmental Environmental Monitoring Monitoring Report Report 24 24
Aquatic Pathway Aquatic Pathway Monitoring downstream downstream of of the the SSES.
SSES. Most Most compared compared to to .:..0.11
.:..0.11 to to 1.91 1.91 forfor 2003.
2003.
radionuclides discharged radionuclides discharged from from the the SSES SSES Comparison of Comparison of the the 2004 2004 meanmean iodine-iodine-CTBD are CTBD are at at such such low low levelslevels in in the the 131 activity 131 activity of of 0.49 0.49 peinpein for for allall downstream river downstream river water water that, that, even even with with indicator locations indicator locations 'to 'to the the average average of of the the the sensitive the sensitive analyses analyses perfonned, perfonned, they they annual control annual control mean mean of of 0.36 0.36 pCill pCill for for cannot be cannot be detected.
detected. pre-operational years pre-operational years suggests suggests activity activity detected slightly detected slightly above above the the When the'radioactivity levels When the'radioactivity levels from from thethe preoperational control.
preoperational control.
CTBD samples CTBD samples throughout throughout the the yearyear are are
averaged with averaged with those those obtained obtained from from Throughout Throughout the the course course of of aa year, year, iodine-iodine-actual downstream actual downstream monitoringmonitoring 131 is 131 is typicaIly typicaIly measured measured at at levels levels in in locations, the locations, the result result is is an an overall overall excess of excess of analysis analysis .MDCs .MDCs in in some some
.. indicator indicator location location average average that that is is too too samples obtained samples obtained from from control control surface surface high to high to be be representative representative of of the the actual actual water monitoring water monitoring locationslocations on on the the average radioactivity average radioactivity levels levels of of the the Susquehanna River Susquehanna River upstream upstream of of the the downstream river downstream river water.
water. As As the the SSES as SSES as well well as as indicator indicator locations locations following discussions following discussions are are reviewed, reviewed, downstream of downstream of the the SSES.
SSES. As As consideration should consideration should be be givengiven to to this this determined by determined by measurements measurements of of inflation of inflation of average average radioactivity radioactivity levels levels samples obtained samples obtained by by the the SSES SSES REMP, REMP, from the from the inclusion inclusion of of CTBD CTBD (location(location the mean the mean iodine-131 iodine-131 activity activity levellevel from, from, 2S7/6S7) results 2S7/6S7) results i~ the the indicator indicator data data the CTBD the CTBD for a)) of for a)) of 2004 2004 was was ..
that is that is averaged.
averaged. approximately 0.75 approximately 0.75 pCi/} pCi/} compared compared to to the control the control mean mean of of 0.36 pCi/} for 0.36 pCi/} for 2004.
2004.
Surface Water Surface Water Gross Gross Beta Beta Monthly Monthly samples samples from from all all surface surface water water Iodine-131 from Iodine-131 from the the discharge discharge of of locations were locations were analyzed analyzed for for ,, medical medical wastes wastes into into the the Susquehanna Susquehanna concentrations of concentrations of gross gross beta beta activity activity River upstream River upstream of of the the SSES SSES is is drawn drawn (Table 1-2).
(Table 1-2). TheThe 2004 2004 indicator indicator values values into the into the SSES SSES cooling cooling tower tower basins basins ranged from ranged from 1.141.14 to to 15.9 15.9 pein,'pein,' "" through the through the SSES SSES River River WaterWater Intake Intake compared to compared to 2.42 2.42 to to 15.9 15.9 peillpeill for for 2003.
2003. Structure. It Structure. It is is reasonable reasonable to to assume assume Comparison of Comparison of the the '2004
'2004 mean mean grossgross that concentration that concentration of of the the already already beta activity beta activity of of 5.7 5.7 peill peill for for all all indicator indicator existing iodine-131 existing iodine-131 in in the the cooling cooling towertower locations to locations to the the average average of of the the annual annual basins occurs basins occurs as as itit does does forfor other other control mean control mean of of 4.0 4.0 pCin pCin for for pre-pre- substances found substances found in in the the river.
river. For For operational years operational years suggests suggests activity activity ,, example, the example, the SSES SSES routinely routinely assumes assumes detected slightly detected slightly above above the the concentration factors concentration factors in in the the basin basin forfor preoperational control.
preoperational control. calcium of calcium of four four to to five five times times the the concentrations in concentrations in the the river river water water Surface Water Iodille-131 ii;;"" entering the entering the basins,'
basins,' basedbased on on past past Bi-weekly Bi-weekly samples samples from from surfacesurface waterwater measurements. This measurements. This concentrating concentrating locations (except locations (except monthly monthly for for the the effect occurs effect occurs because because of of the the evaporation evaporation LTAW)
LTA W) were were analyzed analyzed for, for, of the of the water water in in the the basins, basins, leaving leaving concentrations ofiodine-131'activity concentrations ofiodine-131'activity behind most behind most dissolved dissolved and and suspended suspended ..
(Table 1-3).
(Table 1-3). TheThe 2004 2004 indicator indicator vaiues vaiues materials in materials in the the unevaporated unevaporated water water ranged from ranged from -0.3-0.3 to to 1.39 1.39 pei/) pei/) remaining in remaining in the the basins.
basins. If If aa 2S 2S :: 2004 2004 Radiological Radiological Environmental Environmental MonitoringMonitoring ReportReport
Aquatic Pathway Monitoring concentration concentration factor factor ofof four four for for iodine-iodine- discharged from discharged from thethe SSES SSES to to the the 131 were 131 were to to bebe applied applied to to the the 2004 2004 Susquehanna Susquehanna River River during during 2004.2004.
mean iodine-131 mean iodine-131 activity activity level level forfor the the control samples control samples from from thethe Susquehanna Susquehanna Surface Water Tritium River, aa mean River, mean concentration concentration of of 1.44 1.44 Monthly samples Monthly samples from from all all surface surface waterwater pCilJiter for pCilJiter for iodine-131 iodine-131 in in the the basin basin locations locations were were analyzed analyzed for for water and water and thethe water water being being discharged discharged concentrations of concentrations of tritium tritium activity activity from the from the basins basins would would be be expected.
expected. The The 1-2). Tritium (Table 1-2).
(Table Tritium was was detected detected in in actual 2004 actual 2004 mean mean of of 0.75 0.75 pCi/1 pCi/1 forfor the the both the both the indicator indicator and and control control locations locations CTBD mean CTBD mean is is about about half half the the expected expected MOC. The above MOC.
above The 20042004 indicator indicator valuesvalues mean.
mean. ranged from ranged from -71.5
-71.5 to to 18400 18400 pCW pCW compared to compared to -35.4
-35.4 to to 16,600 16,600 for for 2003.
2003.
Because iodine-131 is Because iodine-131 is radioactive, radioactive, Comparison of Comparison of the the 2004 2004 mean mean tritium tritium unlike the unlike the calcium calcium that has been that has been activity of activity 1,575 pC of 1,575 pC inin for for all all indicator indicator measured. iodine-131 measured. iodine-131 is is removed removed from from locations to locations to the the average average of of the the annual annual the water the water while while it it is is in in the the basins basins preoperational control preoperational control mean mean of of 171 171 through the through the radioactive radioactive decay decay process.
process. pCin indicates pCin indicates aa contribution contribution of of tritium tritium Thus, it Thus, it might might be be expected expected that the net that the net activity from activity from the the SSES.
SSES.
concentration factor concentration factor forfor iodine-131 iodine-131 would be would be somewhat somewhat less less than than that that for for Refer Refer to to Figure Figure 10 10 which which trends trends Tritium Tritium calcium, considering calcium, considering this this ad<ditional ad<ditional activity levels activity levels separately separately for for surface surface removal process.
removal process. The The extent extent to to which which water indicator water indicator and and control control locations locations < <
the iodine-131 the iodine-131 concentration concentration factor factor is is from 1972 from 1972 through through 2004.2004.
than that less than less that forfor calcium calcium wouldwould depend depend on the on the mean mean residence residence time time for for the the The much higher The much higher levels levels of of tritium tritium water in water in the the basins basins compared compared to to iodine-iodine- observed in observed in the the CTBD CTBD line line (location (location 131's radioactive 131's radioactive half-life half-life -- thethe greater greater 2S7/6S7), when 2S7/6S7), when averaged averaged with with thethe low low the ratio the ratio ofof the the mean mean residence residence time time to to levels from levels from ihe ihe downstream downstream Jocation Jocation the half-life, the half-life, the the smaller smaller the the sample analysis 6S5 sample 6S5 analysis results results distort distort thethe concentration factor.
concentration factor. A A mean mean residence residence real environmental real environmental picture. picture. The The meanmean time for time for water water in in the the basins basins is is expected expected tritium activity tritium activity level level fromfrom indicator indicator to be to be about about two two days.
days. This This is is only only about about location 6SS location 6SS forfor 2004 2004 was was 67.267.2 one-fourth of one-fourth of the the approximately approximately eight- eight- pCi/Jiter, which pCi/Jiter, which is is Jess Jess than than the the mean mean day half-life day half-life of of iodine-131.
iodine-131. Thus, Thus, tritium activity tritium activity of of 75.7 75.7 pCi/1 pCi/1 for for the the radioactive decay radioactive decay wouldwould not not bebe control location control location and and is is within within the the range range expected to expected to reduce reduce the the concentration concentration of prior of prior operational operational and and preoperational preoperational factor for factor for iodine-131 iodine-131 by by aa large large amount.
amount. periods.
periods.
Therefore. the Therefore. the difference difference between between the the 2004 mean 2004 mean iodine-131 iodine-131 activity activity of of about about Tritium activity levels Tritium activity levels reported reported for for 0.75 pCill 0.75 pCill in in the the CTBD CTBD and and the the 2004 2004 2S716S7 are are from from the the discharge discharge line line mean iodine-I31 mean iodine-I31 activity activity forfor the the control control to dilution prior to prior dilution in in the the river.
river. The The highest highest location of location of 0.36 0.36 pCi/1pCi/1 should should be be the the quarterly average quarterly average tritium tritium activity activity result of result of concentration concentration in in the the basins.
basins. reported at reported at 2S7/6S7 during during 2004 2004 was was fodine-131 was fodine-131 was not not reported reported in in water water approximately 7,888 approximately 7,888 pCi/liter pCi/liter for for the the first quarter.
first quarter. This This is is well well below below the the 200~ Radiological Environmental Radiological Environmental Monitoring Monitoring Report Report 26 26
Aquatic Pathway Aquatic Pathway !tlonitoring
!tlonitoring NRC non*routine reporting NRC reporting levels levels for for discharges from discharges from the the SSES SSES to to the the
- I quarterly average activity quarterly average activity levels levels of of ""
- Susquehanna Susquehanna River. River.
\....J 20.000 pCilliter 20.000 pCilliter whenwhen aa drinking drinking waterwater pathway exists pathway exists or or 30,000 30,000 pCi/liter pCi/liter when when ** Appendix G.
Appendix G. Table Table G G page page 3 3 and and 4 4 no drinking no drinking water water pathway pathway exists.
exists. of 13 shows of 13 shows aa summary summary of of the the 2004 2004 ""
drinking water drinking water data.
data.
The tritium activity The tritium activity reported reported in in the the CTBD line CTBD from location line from 2S7/6S7 is location 2S7/6S7 is ** Appendix Appendix H. H. Table Table H H 55 through through H H 77 attributable to attributable to the the SSES.
SSES. Refer Refer to to the the shows comparisons shows comparisons of of gross gross alpha.
alpha.
"Dose from "Dose from the the Aquatic Aquatic Pathway" Pathway" gross beta gross beta and and tritium tritium activity activity in in discussion at discussion at the the end end ofof this this section section forfor drinking water drinking water forfor 2004 2004 against against past past additional infonnation additional infonnation on on thethe projected projected years' data.
years' data.
dose to dose to the the population population from from tritium tritium andand other radionuclides other radionuclides in in the the aquatic aquatic ** Appendix Appendix I, I, Table Table 1-4 1-4 shows shows pathway attributable pathway attributable to to the the SSES.
SSES. specific results specific results of of gross gross beta, beta, gross gross alpha. tritium alpha. tritium andand iodine-131 iodine-131 No No gamma*emitting radionuclidesradionuclides were were analyses of analyses of drinking drinking waterwater detected in detected in surface surface water water samples samples above above MDC, with MDC, with the the exceptions exceptions of of Drinking Water Drinking Water GrossGross AlpJzaAlpJza potassium-40 and potassium-40 and iodine-131.
iodine-131. Monthly Monthly samples samples fromfrom the"12iI2-the"12iI2-drinking water drinking water location location were'analyzed were'analyzed
Drinking Water Drinking Water for concentrations for concentrations of of gross gross alpha alpha
Drinking Drinking water water waswas monitored monitored during during activity (Tables activity (Tables 1-41-4 Appendix Appendix I). I). No No 2004 'at 2004 'at the the Danville Danville Water Water Company's Company's alpha activity alpha activity waswas detected detected above:MDC above:MDC facility 26 facility 26 miles miles WSW WSW of of the the SSES SSES on on for 2004.
for 2004. TheThe 2004 2004 values values ranged ranged fromfrom the Sus'quehanna the Sus'quehanna River River at at location location -0.492 to
-0.492 to 0.844 0.844 pCill pCill compared compared to to 12H2.
12H2. -0.654 to
-0.654 to 1.37 1.37 for for 2003.
2003.
There are There are no no known known drinking drinking water:
water: Drinkillg Water Drinkillg Water GrossGross Beta Beta supplies in supplies in Pennsylvania Pennsylvania on on the the Monthly Monthly samples samples fromfrom the the 12H2 12H2 Susquehanna River Susquehanna River upstream upstream of of the the drinking \vater drinking \vater location location were were analyzed analyzed
'SSES 'and
'SSES 'and therefore therefore no no drinking drinking waterwater for concentrations for concentrations of of gross gross beta beta activity activity control monitoring control monitoring locations.
locations. Danville Danville .. (Table 1-4).
(Table 1-4). -Beta
-Beta activity activity waswas detected detected .'.'
drinking water drinking water analysis analysis results results may may be be in the in the 12H2 12H2 location location above above :MOe:MOe for, for, compared to compared to the the results results for for surface surface 2004. The 2004. The 2004 2004 values values ranged ranged from from water control water control monitoring monitoring locations.
locations. ,, ,, 0.735 to 0.735 to 3.09 3.09 pCin pCin compared compared to to 0.898 0.898 to 4.26 to 4.26 for for 2003.
2003.
Refer Refer to to the the following following for for results results ofof ',)_
',)_
surface water surface water analyses analyses forfor 2004:
2004: Gross Gross beta beta activity activity has has been been monitored monitored in drinking in drinking water water since since 1977.
1977. GrossGross
- Figure Figure 11 11 trends trends gross gross betabeta activity, activity, beta activity beta activity is is typically typically measured measured at at levels for levels for drinking drinking water water location location levels exceeding levels exceeding the the MDCs MDCs in in drinking drinking 12H2 from 12H2 from 1977 1977 through through 2004;2004; No No .. water samples.
water samples. The The 2004 2004 meanmean grossgross gross beta gross beta activity activity in in drinking drinking water water beta activity beta activity ofof 1.9 1.9 pCill pCill isis below below the the during 2004 during 2004 is is attributed attributed to to liquid liquid mean gross mean gross beta beta activity activity of of 2.3 2.3 for for 2003 2003 27 27 ,, 2004 2004 Radiological Radiological Enl'ironmcntal Enl'ironmcntal Monitoring Monitoring Report Report
Aquatic Pathway it/onitoring but is within but is within the the range range of of the the Fish preoperational (( 1977-81) preoperational 1977-81) values values of of 2.2 2.2 Refer to Refer to the the following following for for results results of of fish fish to 3.2 to 3.2 pC/I.
pC/I. analyses analyses forfor 2004:
2004:
Drinking Water Iodine-131 ** Table Table G G page page 5 of 13 5 of 13 shows shows aa Bi-weekly samples from Bi-weekly samples from the the 12H2 12H2 summary of summary of the the 2004 2004 fish fish data.
data.
drinking water drinking water location location werewere analyzed analyzed ** Table H Table H 88 shows shows comparisons comparisons of of for concentrations for concentrations of of iodine-131 iodine-131 activity activity potassium-40 monitoring potassium-40 monitoring results results (Table 1-4).
(Table 1-4). No No iodine-131 iodine-131 activity activity was was against past against past years years data.
data.
detected in detected in drinking drinking waterwater samples samples ** Table 1-5 Table 1-5 shows shows specific specific results results of of above :MOCs above :MOCs for for 2004.
2004. The The 2004 2004 values values gamma spectroscopic gamma spectroscopic analyses analyses of of ranged from ranged from -- 0.17 0.17 toto 0.49 pCi/1 0.49 pCi/1 fish.
fish.
compared to compared to -- 0.16 0.16 to to 0.58 0.58 for for 2003.
2003.
Fish Gamma Fish Gamma Spectroscopic Spectroscopic Drinkillg Water Drinkillg Water Tritillm Tritillm Semi-annual Semi-annual samples samples from from thethe indicator indicator Monthly samples from Monthly samples from thethe 12H2 12H2 (IND) and (IND) and control control (2H)(2H) fish fish locations locations drinking water drinking water location location were were analyzed analyzed were analyzed were analyzed for for concentrations concentrations of of for concentrations for concentrations of of tritium tritium activity activity gamma activity gamma activity (Table (Table 1-5).
1-5).
(Table 1-4).
(Table 1-4). Tritium Tritium activity activity waswas detected above:MOC detected above:MOC in in 33 out out ofof 12 12 Three species of Three species of fish fish were were sampled sampled at at drinking water drinking water samples samples in in 2004. The 2004. The each of each of one one indicator indicator location location and and one one 2004 values 2004 values ranged ranged from from -17.5
-17.5 to to 195 195 control location control location on the Susquehanna on the Susquehanna pCill compared pCill compared to -7.67 to to -7.67 to 193 193 for for River in River in April April 20042004 and and again again in in 2003.
2003. October 2004.
October 2004. The The species species included included the following:
the following: small small mouth mouth bass, bass, The 2004 mean The 2004 mean tritium aciivity of tritium aciivity of 74.1 74.1 channel catfish channel catfish andand shorthead shorthead redhorse.
redhorse.
pCin for pCin for drinking drinking waterwater was was higher higher than than In addition, In addition, oneone largemouth largemouth bass bass was was the mean the mean tritium tritium activity activity of of 64 64 pCi/1 pCi/1 for for sampled from sampled PPL's LT from PPL's LTA AW W in in October October 2003 but 2003 but isis less less than than the the preoperational preoperational 2004. A 2004. A total total ofof 1313 fish fish were were collected collected (1977-81) values (1977-81) values of of 101 101 to to 194 pCi/1.
194 pCi/1. and analyzed.
and analyzed.
The 2004 The 2004 mean mean tritium tritium activity activity level level for for drinking water drinking water is is less less than than the the 2004 2004 The The onlyonly gamma-emitting gamma-emitting radionuclide radionuclide mean tritium mean tritium activity activity level level ofof 75.7 75.7 pCi/J pCi/J reported in reported in excess excess of of analysis analysis :MOCs
- MOCs in in for the for the surface surface water water control control location.
location. fish during fish during 2004 2004 was was naturally naturally occurring potassium-40.
occurring potassium-40. The The 2004 2004 Drinking Water Gamma values ranged values ranged fromfrom 2,920 2,920 to to 4,120 4,120 Spectroscopic pClkg compared pClkg compared to to 1,300 1,300 to to 4,389 4,389 for for With the With the exception exception of of potassium-40, potassium-40, no no 2093. The 2093. The 2004 2004 indicator indicator and and control control gamma-emitting radionuclides were gamma-emitting radionuclides were means for means for the the activity activity levels levels of of detected in detected in drinking drinking waterwater samples samples potassium-40 in potassium-40 in fish fish were were 3,531 3,531 pCilkg pCilkg above the above the MDC.
MDC. .. and 3,475 and 3,475 pCilkg, pCilkg, respectively.
respectively.
Naturally occurring Naturally occurring potassium-40 potassium-40 in in fish is fish is not not attributable attributable to to the the liquid liquid discharges from discharges from thethe SSES SSES to to the the Susquehanna River.
Susquehanna River.
2004 Radiological 2004 Radiological Environmental Environmental Monitoring Monitoring Report Report 28 28
Aquatic Pathway Aquatic Pathway Monitoring Monitoring preoperational years.
preoperational years. TheThe cesium-137 cesium-137 Sediment in sediment is in sediment is attributed attributed to to residual' residual' Refer Refer to to the the following following for for results results of of fa))out from fa))out from past past atmospheric atmospheric nuclear nuclear sediment analyses sediment analyses for 2004:
for 2004: weapons tests.
weapons tests.
- Appendix Appendix G, G, Table Table G G pages pages 66 andand 7 7 Dose Dose from from the the Aquatic Aquatic of 13 of 13 shows shows aa summary summary of of the the 2004 2004 Patlnvay Patlnvay sediment data.
sediment data.
Tritium Tritium was was the the only only radionuclide radionuclide
- Appendix Appendix H, H, Tables Tables H 9,10,11 and H 9,10,11 and identified in identified in 2004 2004 by by the the SSES SSES REMP REMP 12 shows 12 shows comparisons comparisons of of in the in the aquatic aquatic pathway pathway that that was was potassium-40, radium potassium-40, radium -- 226, 226, attributable to attributable to SSES SSES operation operation and and also also thorium -- 228, thorium 228, and and cesium cesium -- 137 137 included in included in the the pathway pathway to to man.
man. ..
monitoring results monitoring results against against past past years' data.
years' data. The total tritium The total tritium activity activity released released from from the SSES the SSES for for thethe year year was was estimated estimated
- Appendix Appendix I, I, Table Table 1-61-6 shows shows based on based REMP monitoring on REMP monitoring resultsresults for for specific results specific results of of gamma gamma use in use in projecting projecting maximum maximum doses doses to to the the spectroscopic analyses spectroscopic analyses of of sediment sediment public.
public. ~ .. _ _
samples.
samples.
The annual mean The annual mean activity activity level level of of Sedimellt Gamma Sedimellt Gamma Spectroscopic Spectroscopic tritium in tritium in the the CTBD CTBD line line (monitoring (monitoring Semi-annual samples Semi-annual samples from from al1 al1 sediment sediment .. location location 2S7\6S7) 2S7\6S7) for for 2004 2004 was was 4,483 4,483 locations locations were were analyzed analyzed for for pCi/I. The pCi/I. The annual annual meanmean activity activity level level concentrations of concentrations of gamma gamma activity activity (Table (Table for the for the river river upstream upstream of of the the SSES SSES 1-6). Natural1y 1-6). Natural1y occurring occurring potassium-40, potassium-40, (monitoring location (monitoring location 6S6) 6S6) was was radium-226, and radium-226, and thorium-228 thorium-228 were were approximately 76 approximately 76 pein.
pein. Thus, Thus, the the measured at measured at activity activity levels levels above above :MDCs
- MDCs difference in difference in the the mean mean activity activity levels levels for.
for.
in aU in aU shoreline shoreline sediment sediment sampJes sampJes in in these two these two locations locations was was about about 44074407 2004. The 2004. The naturally naturally occurring occurring pCin. The pCin. The annual annual meanmean flowflow rate rate for for radionuclides in radionuclides in sediment sediment are are not not the CTBD the CTBD line was 8,818 line was 8,818 gpm.gpm. UsingUsing attributable to attributable to the the Jiquid Jiquid discharges discharges the proper the proper unitunit conversions conversions and and from the from the SSES SSES to to the the Susquehanna Susquehanna multiplying 8,818 multiplying 8,818 gpm gpm times times 4,407 4,407 River.
River. pCill yieJds pCill yieJds aa value value ofof 77.3 77.3 curies curies for for the estimate the estimate of of tritium tritium released released from from Cesium-137 Cesium-137 was was measured measured at at activity activity SSES during SSES during 2004.
2004. ThisThis estimate estimate is is levels exceeding levels exceeding analysis analysis :MDCs
- MDCs in in 11 of of 15.2 curies 15.2 curies moremore thanthan the the amount amount of of 88 shoreline shoreline sediment sediment samplesample analyses analyses inin tritium detennined tritium detennined by by effluent effluent 2004. The 2004. The 2004 2004 indicator indicator andand control control monitoring to monitoring to have have been been released released to to the the means for means for cesium-137 cesium-137 activity activity levels levels in in river by river by the the SSES SSES in in 2004.
2004.
sediment were sediment were 22 22 pCilkg pCilkg andand 6666 pCilkg.
pCilkg.
The 2004 The 2004 indicator indicator and and control control means means Given the Given the total total tritium tritium activity activity released, released, are Jess are Jess than than the the average average of of the maximum whole-body the maximum whole-body and and organ organ corresponding annual corresponding annual means means forfor both both doses to doses to hypothetical hypothetical exposedexposed prior operational prior operational as as well well as as individuals in individuals in four four age age groups groups (adult, (adult, 29 29 2004 Radiological 2004 Radiological Environmental Environmental Monitoring Monitoring ReportReport
M01litoring Aquatic Pathway M01litoring teenager, child, and teenager, child, and infant) infant) were were detennined according detennined according to to the the methodology of methodology of the the Offsite Offsite Dose Dose Calculation manual Calculation manual using using the the RETDAS RETDAS computer program.
computer program. This This isis in in accordance with accordance with SSES SSES Technical Technical Requirement 3.11.4.1.3.
Requirement 3.11.4.1.3.
The maximum dose The maximum dose obtained obtained fromfrom the the of tritium ingestion of ingestion tritium was was estimated estimated at at the the nearest downriver nearest downriver municipal municipal water water supplier via supplier via the the drinking drinking water water pathway pathway and near and near the the outfall of the outfall of the SSES SSES discharge to discharge to the the Susquehanna Susquehanna RiverRiver via via the fish the fish pathway.
pathway. TheThe maximum maximum whole whole body and body and organ organ doses doses (child)
(child) were were each each calculated as calculated as 0.0015 0.0015 mrem.
mrem.
-...J
-...J 2004 Radiological 2004 Radiological Environmental Environmental Monitoring Monitoring Report Report 30 30
FIGURE 9 FIGURE 9 -- GROSS GROSS BETA BETA ACTIVITY ACTIVITY IN IN SURFACE WATER SURFACE WATER pCi/Liter pCi/Liter 20 ~----------------~----------------------------------------------~
18 18 PREOPERA TIONAL PREOPERA TIONAL OPERA TIONAL OPERA TIONAL 16 16 14 14 12 10 10 8
8 66 4
22 o+---------------~~----------------------------------~----------~
-2
-2
-4 +-~~~~~~~--r_~~~~~~~~~--~~~~~~~~~~--~~~
t-,'"
t-,"> t-,f\, ""f\,~ ~"
ft," ~",
ft,'" ~",
ft,"> ;-. ""rf'
""rfJ ~" ~", ~",
~"> ~f\, ~~ ~" ~", ~",
~">
~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~
- Indicator - Control
FIGURE 10 FIGURE 10 -- TRITIUM TRITIUM ACTIVITY ACTIVITY IN IN SURFACE SURFACE WATER WATER pCi/Liter pCi/Liter 3000 ,-----------------------~------------------------------~~----------~
~----------------------~------------------------------~~------------,
PREOPERATIONAL PREOPERATIONAL OPERATIONAL OPERATIONAL 2500 2500 2000 2000 1500 1500 Unit 2 Unit 2 1000 1000 Criticality
~
-500 +-~~~~~~~~--~~~~~~~~~~--~~,_~~~~~~~~--~~~
+-~~~~~~~--~~~~~~~~~~~--~~~~~~~~~~~~~~~
t..'V t.."'-f t..b.
t..b4 t..'o t..'o t..'b t..'b ~~
~ {' ~ ~
{' ~
-- Indicator Indicator -- Control Control ell Cll
cc (( ((
FIGURE 11 FIGURE 11 -- GROSS GROSS BETA BETA ACTIVITY ACTIVITY IN IN DRINKING WATER DRINKING WATER pCi/Lifcr pCi/Lifcr 10~------------~~--------------------------------------------------~
99 PREOPERATIONAL PREOPERATIONAL OPERATIONAL OPERATIONAL 88 7
7 6
6 55 4
4 33 2
2 1
1 O+-~~~~~~~~--r-T-~-r~--r-~~~~--~~~~__ __~T-~-r~--r-T
~
t>."
t>."
Atmospheric Pathway Atmospheric Pathway Monitoring Monitoring INTRODUCTION INTRODUCTION Sampling and Sampling and Analysis Analysis Atmospheric monitoring by Atmospheric monitoring by the the SSES SSES Air Air REMP involves REMP involves the the sampling sampling and and The SSES REMP The SSES REMP monitored monitored the the air air at at analysis of analysis of air.
air. Because Because the the air air isis the the four indicator four indicator locations locations and and two two control control first medium first medium that that SSES SSES ventvent releases releases loc~ltions during during 2004.2004. The The SSES SSES enter in enter in the the pathway pathway to to man, man, it it is is Technical Requirements Technical Requirements require require fundamental that fundamental it be that it be monitored.
monitored.
monitoring at monitoring at only only aa total total of of five five sites.
sites.
Mechanisms do Mechanisms do exist exist for for the the transport transport Monitoring is Monitoring is required required at at three three locations locations of airborne of airborne contaminants contaminants to to other other mediamedia at the at the SSES SSES sitesite boundary boundary in in different different and their and their concentration concentration in in them.
them. 'For 'For sectors with sectors with the the greatest greatest predicted predicted example, airborne example, airborne contaminants contaminants may may sensitivities for sensitivities for the the detection detection of of SSES SSES move to move to the the terrestrial terrestrial environment environment and and releases. Monitoring releases. Monitoring must must be be performed performed concentrate in concentrate in milk.
milk. Concentrations Concentrations of.: of.:
at the at the community community in in the the vicinity vicinity ofof the the radionuclides 'can radionuclides 'can make make the the sampling' sampling' SSES with SSES with the the greatest greatest predicted predicted and analysis and analysis of of media media like like milk milk moremore
sensitivity. A sensitivity. A control10cation control10cation that that is is sensitive approaches sensitive approaches for for the the detection detection of of expected to expected to be be unaffected unaffected by by any any routine routine radionuciides, such radionuciides, such asas iodine-13I, iodine-13I, in in the the SSES releases SSES releases mustmust be be monitored.
monitored.
pathway to pathway to man man thanthan the the monitoring monitoring of of air directly.'
air directly.' *(pPL also also samples samples milk; milk; Airborne particulates Airborne particulates were were collected collected on on refer to refer to the the Terrestrial Terrestrial Pathway Pathway glass fiber filters glass fiber filters using using low low volume volume Monitoring section Monitoring section of of this this report.)
report.)
(typicaUy 2.0 (typicaUy 2.0 toto 2.5 2.5 cfm cfm sampling sampling rates) rates)
Nevertheless, the Nevertheless, the sensitivity sensitivity of of air air air samplers air samplers thatthat run run contiriuously.
contiriuously. Air Air monitoring can monitoring can be be optimized optimized by by the the iodine samples iodine samples werewere collected collected on on proper selection proper selection of of sampling sampling techniques techniques charcoal cartridges, charcoal cartridges, placedplaced downstream downstream and the and the choice choice of of the the proper proper types types of of of the of the particulate particulate filters.
filters.
analyses for analyses for the the collected collected samples.
samples.
Particulate filters and Particulate filters and charcoal charcoal Scope Scope cartridges were cartridges were exchanged exchanged weekly weekly 'at,
'at, the the air monitoring air monitoring sites.
sites. Sampling Sampling timestimes Air samples Air samples were were collected collected on on were recorded were recorded on on elapsed-time elapsed-time ~eters.
particulate filters and particulate filters and charcoal charcoal Air sample Air sample volumes volumes for for particulate particulate cartridges at cartridges at indicator indicator locations locations 3S2, filters and filters and charcoal charcoal cartridges cartridges werewere ....
12S1, 13S6 12S1, 13S6 andand 12EI, 12EI, andand control control measured with measured with dry-gas dry-gas meters.
meters.
locations 6Gl locations 6Gl and and 8Gl.
8Gl. ,,
Air filters Air filters were were analyzed analyzed weeklyweekly forfor gross beta activity, gross beta activity, thenthen composited composited quarterly and quarterly and 'analyzed
'analyzed fort~e activities activities of gamma-emitting of gamma-emitting radionuclides.
radionuclides. The. The.
charcoal cartridges charcoal cartridges were were analyzed analyzed weekly for weekly for iodine-131.
2004 Radiological 2004 Radiological Environmental Environmental Monitoring Monitoring Report Report 34 34
Atmospileric Pathway lUonitoring Monitoring Results Monitoring Results pCilm33 indicates pCilm indicates no no appreciable appreciable effects effects from the from the operation operation of of SSES~ ..
Air Particulates Gross beta Gross beta activity activity is is normally normally Refer Refer to to the the following following for for results results of of air air measured measured at at levels levels in in excess excess of of the the particulate analyses particulate analyses for for 2004:
2004:
analysis MDCs analysis MDCs on on the the fiber fiber filters.
filters. The The highest gross highest gross betabeta activity activity levels levels that that
- Figure Figure 12 12 trends trends gross gross betabeta activities' activities' been measured have been have measured duringduring the the separately for separately for air air particulate particulate operational period operational period of of the the SSES SSES werewere indicator and indicator and control control locations locations fromfrom obtained in obtained in 1986 1986 foHowing foHowing the the 1974 through 1974 through 2004.2004.
Chemobyl accident Chemobyl accident in in the the former former Soviet Soviet Union.
Union.
- Appendix G, Appendix G, Table Table G G pages pages 5,5, 88 and and 99 of of 1313 shows shows aa summary summary of of the the Note that prior Note that prior to to SSES SSES operation,.
operation,.
2004 air 2004 air particulate data.
particulate data. 1982, the before 1982, before the unusually unusually highhigh gross gross beta activities beta activities were were generally generally
- Appendix Appendix H, Tables H H, Tables H 13 13 and and 1414 attributable to attributable to fallout fallout from from atmospheric atmospheric shows comparisons shows comparisons of of gross gross beta beta nuclear weapons nuclear weapons tests. tests. Typical Typical gross gross and BeryIIium-7 and BeryIIium-7 monitoring monitoring results results beta activities beta activities measured measured on on air air against past against past years years data.
data. particulate filters particulate filters are are the the result result oEoE naturally occurring naturally occurring radionuclides radionuclides
- Appendix I,I, Table Appendix Table 1-81-8 shows shows associated with associated with dust dust particles particles suspended suspended specific sample results specific sample results of of gross gross beta beta in the in the sampled sampled air. air. They They areare thus thus analyses for analyses for air air particulate particulate filters.
filters. terrestrial in terrestrial in origin.
origin.
Air Particulate Air Particulate Gross Gross Beta Beta The SSES Technical The SSES Technical Requirements Requirements Weekly Weekly samples samples from from allall air air particulate particulate Manual requires Manual requires radionuclide radionuclide analysis analysis if if filter locations filter locations were were analyzed analyzed for for any weekly any weekly gross gross beta beta result result was was greater greater concentrations of concentrations of gross gross beta beta activity activity than ten than ten times times the the yearly yearly mean mean of of (Table 1-8).
(Table 1-8). Gross Gross beta beta activity activity waswas control sample control sample results.
results. This This condition condition observed at observed all locations at all locations above above MDC MDC did not did not occur occur during during 2004.
2004.
for 2004.
for 2004. The The 2004 2004 values, values, bothboth indicator and indicator and control, control, ranged ranged fromfrom Air Particulate Gamma 33 3.S1E-3 to 3.S1E-3 to 3.66E-2 3.66E-2 pCilmpCilm ,, ~ompared Spectroscopic to 3.59E-3 to 3.59E-3 to to 3.
- 3. 17E-2 17E-2 pCi/m pCi/m for for 2003.
2003.
Quarterly Quarterly gammagamma spectroscopic spectroscopic The 2004 The 2004 mean mean grossgross beta beta activity activity of of measurements of measurements of composited composited filters filters 1.39E-2 pCi/m 1.39E-2 pCi/m33for for all all indicator indicator location location show the often show often the naturally naturally occurring occurring compares to compares to the the average average of of the the annual annual radionuclide beryllium-7.
radionuclide beryllium-7. Occasionally, Occasionally, preoperational control preoperational mean of control mean of 6.20E-2 6.20E-2 3 other naturally other naturally occurring occurring radionuclides, radionuclides, pCi/m indicates pCi/m indicates activity activity detected detected potassium-40 and potassium-40 and radium-226, radium-226, are are also also below the below the preoperational preoperational control.
control. In In observed. Beryllium-7 observed. Beryllium-7 is is cosmogenic cosmogenic in in addition aa comparison addition comparison of of the the 2004 2004 origin, being origin, being produced produced by by the the weekly indicator weekly indicator mean mean forfor beta beta interaction of interaction of cosmic cosmic radiation radiation withwith the the activities of activities 1.39E-2 pCilm of 1.39E-2 pCilm33 compared compared earth's atmosphere.
earth's atmosphere. The The other other twotwo to the to the 2004 2004 control control locations locations of of 1.30E-2 1.30E-2 3S 3S 2004 Radiological 2004 Radiological Environmental Environmental Monitoring Monitoring Report Report
Atmospheric Pathway Atmospheric Pathway Monitoring Monitoring gamma-emitting radionuclides originate gamma-emitting radionuclides originate from soil from soil and and rock.
rock.
Beryllium-7 Beryllium-7 was was measured measured aboveabove analysis MDCs analysis MDCs for for all all quarterly quarterly composite samples composite samples in in 2004.
2004. TheThe 2004 2004 indicator and indicator and control control means means forfor beryllium-7 activity beryllium-7 activity were were 9.16E-2*
pCilm 33 and pCilm and 8.79E-2 pCilm33,,
8.79E-2 pCilm respectively. BerylIium-7 respectively. BerylIium-7 activity activity levels levels for each for each 2004 2004 calendar calendar quarter quarter atat each each monitoring location monitoring location areare presented presented in in Table 1-9 Table 1-9 of of Appendix Appendix I. I. Comparisons Comparisons of2004 bery1lium-7 of2004 bery1lium-7 analysis analysis results results with previous with previous years years maymay bebe found found inin Table H*14 of Table of Appendix Appendix H. H.
No other gamma-emitting No other gamma-emitting radionuclides radionuclides were reported were reported for for air air in in 2004.
2004.
Beryllium-7 is Beryllium-7 is not not attributable attributable to to SSES SSES operation.
operation.
Air Particulate Air Particulate Iodine Iodine lodine-131 lodine-131 hashas been been detected detected infrequently from infrequently from 1976, 1976, when when itit was was first monitored, first monitored, through through 2004.
2004. Since Since operation of operation of the the SSES SSES began began in in 1982, 1982, iodine-131 has iodine-131 has only only been been positively positively detected in detected in air air samples samples in in 1986 1986 due due to to the Chernobyl the Chernobyl accident.
accident. No No iodine':'131 iodine':'131 was reported was reported for for the the 2004 2004 air air monitoring results.
monitoring results.
2004 Radiological 2004 Radiological Em'ironmental Em'ironmental Monitoring Monitoring Report Report 36 36
FIGURE 12 FIGURE 12 -- GROSS GROSS BETA BETA ACTIVITY ACTIVITY IN IN AIR PARTICULATES AIR PARTICULATES E-03 pCi/M3 E-03 pCi/M3 500 ~--------------------~----------------------------------------------------~
CHINESE CHINESE 450 450 PRE OPERA PRE OPERA TIONAL TIONAL OPERATIONAL OPERATIONAL WEAPONS WEAPONS TEST TEST A -- 06/17/74 A 06/17/74 B -- 09/26/76 B 09/26/76 400 400 A A C -- 11/17/76 C 11/17/76 D -- 09/17/77 D 09/17/77 350 350 E -- 03/14/78 E 03/14/78 F -10/15/80 F -10/15/80 300 300 250 250 200 200 oo E 150 150
~ CHERNOBYL CHERNOBYL 4/26/86 4/26/86 II UNIT2 UNIT2 100 100 CRITICALITY CRITICALITY F
F 50 50 0
0 t\1:>.
t\1:>.
~
- Indicator - Control elL-elL.-
Terrestrial Pathway Monitoring INTRODUCTION INTRODUCTION either medium. Sampling either medium. Sampling is is performed performed The following media The following media werewere monitored monitored in in at different at different depths depths nearnear the the surface surface toto the Terrestria1 the Terrestria1 Pathway Pathway in in 2004:
2004: soil,soil, help provide help provide information information on on how how
milk, fruits milk, fruits and and vegetab1es.
vegetab1es. recently certain recently certain radioactive radioactive materials materials may have may have entered entered thethe soil.
soil. Sampling Sampling at at Soil can',be itit great Soil can',be great accumulator accumulator of of man-man- more than more than one one depth depth also also maymay help help made radionuclides that made radionuclides that enter enter it. it. The The ensure the ensure the detection detection of of materials materials that that ..
extent of extent of the the accumulation accumulation in in the the soil soil move relatively move relatively quickly quickly through through the the soil.
soil.
depends of depends ofcourse course onon thethe amount amount of of the the Such quick-moving Such quick-moving materials materials may may have have radioriuclides reaching radioriuclides reaching it, it, but but it it also also already passed already passed through through the the topmost topmost depends on depends on the the chemical chemical naturenature of of those those layer of layer of soil soil at at the the time time ofof sampling.
sampling.
radionuclides'and the radionuclides'and the particular particular characteristics of characteristics of the the soil.
soil. For For example, example, Milk was sampled Milk was sampled at at four four locations locations and and the element the element cesium, cesium, and, and, therefore, therefore, fruit and fruit and vegetable vegetable samples samples were were cesium-137 can cesium-137 can be be bound bound very very tightly tightly toto obtained at obtained at one one location location in in 2004.
2004. SSES SSES clay in clay in soils.
soils. The The amount amount of of clay clay in in soil soil f'f' Technical Requirements Technical Requirements require require that that the' the' ,,
can vary can vary greatly greatly from from one one location location to to SSES REMP SSES REMP samplesample milkmilk at at the the three three another. In'clay another. In'clay soils, soils, cesium-137 cesium-137 may" may" most sensitive most sensitive monitoring monitoring locations locations move very move very slowly slowly andand also also maymay be be taken taken near the near the SSES SSES and and oneone control control location, location, ..
up very up very slowly slowly inin plants plants as as they they absorb absorb distant from distant from thethe SSES.
SSES. SSESSSES Technical Technical soil moisture.
soil moisture. '.'. Requirements only Requirements only require require that that fruit fruit and and
,, vegetables vegetables be be sampled sampled at at locations locations Any medium, such Any medium, such as soH, that as soH, that tends tends to to irrigated by irrigated by Susquehanna Susquehanna River River water water accumulate radioactive accumulate radioactive materials materials can, can, from points from points downstream downstream of of the the SSES SSES also provide also provide more more sensitivity sensitivity for for discharge to discharge to the the River.
River. There There are are only only radionucHde detection radionucHde detection in in the the three 10cations three 10cations within within 10 10 miles miles
,environment than
,environment than those those media media that that downstream of downstream of the the SSES SSES that that have have been been don't.' Such don't.' Such aa medium medium facilitates facilitates the the known to known to irrigate irrigate with with water water fromfrom thethe early identification early identification of of radionuclides radionuclides in in Susquehanna River Susquehanna River during during unusually unusually the environment, the environment, as as well well as as awareness awareness dry periods.
dry periods. These These locations locations do do not not ..
of changes of changes thatthat subsequently subsequently may may occur occur irrigate every irrigate every year.
year. The The Lupini Lupini Farm Farm in in in the in the environmental environmental levels levels of of the the MifflinviJ]e (l2F7)
MifflinviJ]e (l2F7) briefly briefly irrigated irrigated
identified radionuclides.
identified radionuclides. potatoes in potatoes in June June 2004 2004 using using Susquehanna River Susquehanna River water.
water. No No other other The SSES REMP The SSES REMP samples samples soil soil near near four four fields within fields within 1010 miles miles downriver downriver of of of the of the six six REMP air-sampling stations.
REMP air-sampling stations. Susquehanna SES Susquehanna SES were were irrigated irrigated in in The purpose The purpose for for soil soil sampling sampling near. near. thethe 2004, including 2004, including the the Lupini Lupini Farm Farm "Route "Route air sampling air sampling sitessites is is to to make make it it easier easier to to 93 Nescopeck 93 Nescopeck Field" (llD2), Chapin Field" (llD2), Chapin correlate air correlate air sampling sampling results results with with soilsoil Faim "Drake Faim "Drake Field" Field" (11F2),
(11F2), and and Zehner Zehner sampling results sampling results if if any any SSESrelated SSESrelated (lIDl) because Farm (lIDl)
Farm because wet wet weather weather radioactive material radioactive material were were found found in in prevailed much prevailed much of of the the spring spring and and 2004 Radiological 2004 Radiological Em'ironmcntal Em'ironmcntal Monitoring Monitoring Rep?~t 38 38
Terrestrial Pathway Monitoring summer summer duringduring 2004 2004 as as identified identified by by the the be the most be the most sensitive sensitive indicator indicator sites sites 2004 Land 2004 Land UseUse Census Census (Reference (Reference II). II). available for available for the the detection detection of of radionuclides released radionuclides released fromfrom thethe SSES.
SSES.
No requirement No requirement existsexists for for the the SSES SSES Location 10GI Location 10GI is is the the control control location.
location.
REMP REMP to to monitor monitor soil.
soil. All All monitoring monitoring Since there Since there are are four four monitoring monitoring of the of the terrestrial terrestrial pathway pathway that that is is locations, aa total locations, total of of 76 76 cow cow milk milk conducted by conducted by the the SSES SSES REMP REMP in in samples were samples were collected collected in in 2004.
2004.
addition to addition to milk milk and and certain certain fruit fruit and and vegetables is vegetables is voluntary voluntary and and reflects reflects Fruits alld Fruits alld Vegetables Vegetables PPL's wi1lingness PPL's wi1lingness to to exceed exceed regulatory regulatory Potatoes were sampled Potatoes were sampled during during thethe requirements to requirements to ensure ensure thatthat the the public public harvest season harvest season at at one one location location nearnear thethe and the and the environment environment are are protected.
protected. SSES. One SSES. One sample sample was was collected collected at at location 12F7, location 12F7, whichwhich waswas irrigated irrigated with with Scope Scope Susquehanna River Susquehanna River water water fromfrom downstream of downstream of the the SSES SSES during during 2004.
2004.
Soil Soil Soil was sampled Soil was sampled in in September September 2004 2004 in in There are often There are often years years with with adequate adequate accordance with accordance with its its scheduled scheduled annualannual rainfall when rainfall when no no irrigation irrigation is is performed.
performed.
sampling frequency, sampling frequency, at at the the following following four REMP four REMP air air sampling sampling locations, locations, 3S2,3S2, Sample Preservation. _
Sample Preservation. _
12S1, 13S6, 12S1, 13S6, andand 8Gl.
8Gl. Location Location 8Gl 8Gl and Analysis and Analysis was aa control was control sampling sampling location; location; the the remaining sampling remaining sampling sitessites were were indicator indicator All media in All media in the the terrestrial terrestrial pathway pathway are are _ _
locations.
locations. analyzed for analyzed for the the activities activities of of gamma-gamma-emitting radionuclides emitting radionuclides using using gamma gamma .. ..**~
Twelve Twelve soil soil plugs plugs were were taken taken at at selected selected spectroscopy. The spectroscopy. The other other analysis analysis that that is is spots at spots at each each monitoring monitoring location.
location. -The
-The routinely performed routinely performed is is the the plugs were plugs were separated separated intointo "top" "top" radiochemical analysis radiochemical analysis forfor iodine-131 iodine-131 in in (0-2 inches)
(0-2 inches) andand "bottom" "bottom" (2-6 (2-6 inches) inches) milk.
milk.
segments. Each segments. Each set set of of top top and and bottom bottom segments was segments was composited composited to to yield yield 2 2 soil soil Monitoring Results Monitoring Results samples from samples from each each location location for for analysis.
analysis.
Since there Since there are are four four monitoring monitoring Refer to the Refer to the following following for for results results ofof the the locations, aa total locations, of 88 soil total of soil samples samples were were terrestrial pathway terrestrial pathway analyses analyses for for 2004:
2004:
analyzed in analyzed in 2004.
2004.
- Figure Figure 13 13 trends trends iodine-131 iodine-131 Milk Milk activities separately activities separately for for milk milk Milk Milk waswas sampled sampled at at least least monthly monthly at at indicator and indicator and control control locations locations from from the following the following four four locations locations in in 2004:
2004: 1977 through 1977 through 2004. 2004.
lOD1, IOD2, lOD1, IOD2, 12B2 12B2 and and lOG!.
lOG!.
- Appendix Appendix G, G, Table Table G G pages pages 10 10 Milk Milk waswas sampled sampled semi-monthly semi-monthly from from through 13 through 13 shows shows aa summary summary of of the the April through April through October October when when cowscows werewere 2004 terrestrial 2004 terrestrial monitoring monitoring results results more likely more likely toto be be on on pasture.
pasture. Locations Locations for milk, for milk, soil, soil, and and irrigated irrigated foodfood lODl, lOD2, lODl, lOD2, andand 12B2 12B2 are are believed believed to to crop data.
crop data.
2004 Radiological 2004 Radiological Environmental Environmental Monitoring Monitoring Report Report 39 39
Terrestrial Pathway Terrestrial Pathway Monitoring Monitoring are thorium-228 are thorium-228 and and radium-226 radium-226 in in soil, soil,
- Appendix Appendix H, H, Tables Tables HIS HIS through through and beryllium-7 in and beryllium-7 in fruits fruits andand vegetables.
vegetables.
19 show 19 show comparisons comparisons of of terrestrial terrestrial ,.,.
pathway monitoring pathway monitoring results results against against .. Soil Soil past years' past years' data.
data. :: .. Annual samples from Annual samples from thethe SG1, SG1, 3S2,3S2, and 13S6 soil 12S1 and soil locations locations were were
- Appendix Appendix I, I, Tables Tables 1-101-10 through through 12 12 .. analyzed for analyzed for concentrations concentrations of of gamma gamma shows results shows results of of specific specific sample sample emitting nuclides emitting nuclides (Table 1-11). The (Table 1-11). The analyses for analyses for te~estrial pathway pathway following gamma-emitti:ng following gamma-emitti:ng media.
media. radionucHdes are radionucHdes are routine]y routine]y measured measured in in soil at soil at levels levels exceeding exceeding analysis analysis MDCs:MDCs: ..
The only man-made The only man-made radionuclides radionuclides naturally occurring naturally occurring potassium-40, potassium-40, normally expected normally expected at at levels levels inin excess excess ofof thorium-228 and thorium-228 and man-:-made man-:-made cesium-cesium-MDCs in analysis MDCs analysis in the the terrestrial terrestrial 137. The 137. The 2004 2004 analysis analysis results results werewere pathway are pathway are strontium-90 strontium-90 and and cesium-cesium- similar to similar to those those for for previous previous years. No years. No 137. Both 137. Both of of these these radionuclides radionuclides are are other gamma-emitting other gamma-emitting radionuclides radionuclides present in present in the the environment environment as as aa residual residual were reported were reported at at levels levels above above analysis analysis from previous from previous atmospheric atmospheric nuclearnuclear MDCs.
MDCs.
weapons testing.
weapons testing. Strontium-90 Strontium-90 analysesanalyses are not are not now now routinely routinely performed performed for for any any The 2004 means The 2004 means forfor indicator indicator and and media samples media samples in in the the terrestrial terrestrial control1ocation sample control1ocation sample potassium-40 potassium-40 pathway. Strontium-90 pathway. Strontium-90 activity activity would would activity were 14.5 activity were 14.5 pCi/g pCi/g andand 9.3 9.3 pCi/g,*
be expected be expected to to be be found found in in milk.
milk. SSES SSES .. respectively.
respectively. ThisThis isis not not the the result result ofof Technical Requirements Technical Requirements do do not not require require SSES operation SSES operation because because the the potassium-potassium-that milk that be analyzed milk be analyzed for for strontium-90.
strontium-90. 40 is 40 is naturally naturally occuriing.
occuriing.
Strontium-90 analyses Strontium-90 analyses may may be be performed at performed at any any time time if if the the results results ofof The 2004 means The 2004 means forfor indicator indicator and and other milk other milk analyses analyses wouldwould showshow control location control location sample sample thorium-228 thorium-228 detectable levels detectable levels of of fission fission product product activity were activity were 1.0 1.0 pCi/g pCi/g and and 0.70.7 pCi/g, pCi/g, which might activity which activity might suggest suggest the the SSES SSES respectively. Thorium-228 respectively. Thorium-228 in in soil soil is is not not as the as the source.
source. the result the result of SSES operation of SSES operation becausebecause itit is naturally is naturally occurring occurring.. ..
Cesium-137 normally has Cesium-137 normally has been been measured in measured in excess excess of of analysis analysis MDCs* in in The 2004 means The 2004 means forfor indicator indicator and and most soil most soil samples.
samples. control location control location sample sample ces~um-137 activity were activity were 0.03 0.03 pCi/g pCi/g and and 0.110.11 Certain naturally Certain naturally occurring occurring respectively. The pCi/g, respectively.
pCi/g, The 20042004 indicator indicator radionuclides radionuclides are are also also routinely routinely found found values ranged values from -0.015 ranged from -0.015 to to 0.076 0.076 above analysis above analysis MDCsMDCs in in terrestrial terrestrial pCilg, compared pCilg, compared to to -0.021
-0.021 to to 0.096 0.096 pathway media. Potassium-40, pathway media. Potassium-40, aa pCi/g for pCi/g for 2003.
2003. Cesium-137 Cesium-137 in in soil, soil, primordial and primordial and very very long-lived long-lived although man-made, although man-made, is is not not from from the the radionuclide, which radionuclide, which is is terres.trial terres.trial inin operation of operation of the the SSES.
SSES. It It is is residual residual
.. origin, origin, isis observed observed in in all all terrestrial terrestrial from previous fallout from fallout previous atmospheric atmospheric ..
pathway media.
pathway media. OtherOther naturally naturally weapons testing.
nuclear weapons nuclear testing.
occurring radionucIides occurring radionucIides often often observed observed 40 40 2004 Radiological 2004 Radiological Em'ironmcntal Em'ironmcntal Monitoring Monitoring ReportReport
Terrestrial Pathway Terrestrial Pathway Monitoring Monitoring Milk Milk occurring potassium-40 occurring potassium-40 at at 3.95 3.95 pCi/g pCi/g Semi-monthly Semi-monthly or or monthly monthly samples samples from from was the only was the only gamma-emitting gamma-emitting all milk all milk locations locations were were analyzed analyzed for for radionuclide measured radionuclide measured in in fruits fruits and and concentrations of concentrations of iodine-I31 iodine-I31 and and vegetables at vegetables an activity at an activity level level above above gamma emitting gamma emitting nuclide nuclide activity activity (Table (Table MDC during MDC during 2004. An other 2004. An other nuclides nuclides 1-10). No 1-10). No detectable detectable iodine-131 iodine-131 activity activity were less were than the less than the MOC.
MOC.
above MDC above MDC was was observed observed at at any any location for location for 2004.
2004. The The 2004 2004 indicator indicator Potassium-40 Potassium-40 in in fruits fruits and and vegetables vegetables is is values ranged values ranged from from -0.9-0.9 to to 0.54 0.54 pCifl, pCifl, not attributable not attributable to to SSES SSES operation operation compared to compared to -0.17
-0.17 to to 0.44 0.44 pCill pCill for for because it because it is is aa naturally naturally occurring occurring 2003. Iodine-I31 2003. Iodine-I31 has has been been chemically chemically radionucIide.
radionucIide.
separated in separated in milk milk samples samples and and counted counted routinely since routinely 1977. Refer since 1977. Refer to to Figure Figure 13 13 which trends which trends iodine-131 iodine-131 activity activity in in milk milk for indicator for indicator and and control control locations locations separately from separately from 1977 1977 through through 2004.
2004.
The preoperational The preoperational years years 1976, 1978, 1976, 1978, and 1980 were and 1980 were exceptional exceptional years years in in the the sense that sense that iodine-131 iodine-131 activity activity waswas observed in observed in excess excess of of MDCs MDCs due due to to faHout from faHout from atmospheric atmospheric nuclear nuclear weapons testing.
weapons testing. Iodine-131 Iodine-131 activity activity was also was also measured measured at at levels levels exceeding exceeding MDCs in MDCs in milk milk samples samples in in 1986 1986 in in the the vicinity of vicinity of the the SSES SSES as as aa result result ofof the the Chemobyl incident.
Chemobyl incident.
With the With the exception exception of of the the naturally naturally occurring potassium-40, no occurring potassium-40, no gamma-gamma-emitting radionuclides emitting radionuclides were were measured measured in excess in excess of of analysis analysis MDCs MDCs in in 2004.
2004.
The 2004 The 2004 means means for for indicator indicator and and control location control location sample sample potassium-40 potassium-40 were 1,401 activity were activity 1,401 pCiniter pCiniter and and 1,455 1,455 pCilJiter, respectively.
pCilJiter, respectively. The The potassium-potassium-40 activity 40 activity in in milk milk is is not not attributable attributable to to SSES operation SSES operation becausebecause it is naturally it is naturally occurring.
occurring.
Fruits alld Fruits alld Vegetables Vegetables One potato sample One potato sample was was col1ecled col1ecled from from the 12F7location the 12F7location and and analyzed analyzed for for concentrations of concentrations of gamma gamma emitting emitting nuclide activity nuclide activity (Table 1-12). NaturaHy (Table 1-12). NaturaHy 2004 Radiological 2004 Radiological Environmental Environmental Monitoring Monitoring Report Report 41 41
cc cc ((
FIGURE 13 FIGURE 13 -- IODINE-131 IODINE-131 ACTIVITY ACTIVITY IN IN MILK MILK pCi/Liter pCi/Liter 100 100 CHINESE CHINESE WEAPONS WEAPONS TEST TEST 90 90 09/12177 A- 09/12177 A-PRE-PRE- B -- 03/14178 B 03/14178 OPERATIONAL OPERATIONAL OPERATIONAL OPERATIONAL -10/15/80 C -10/15/80 80 --
80 C 70 70 --
60 60 so so 40 40 A
A CHERNOBYL CHERNOBYL 30 30 4/26/86 4/26/86 20 20 --
UNIT 22 UNIT CRITICAL CRITICAL Y Y
10 10
+
B B
oo nn Do Do C
C
+ **
C!2lndlcator C!2lndlcator ClControl ClControl
Ground Water Ground Water Monitoring Monitoring INTRODUCTION INTRODUCTION Scope Scope Normal operation Normal operation of of the the SSES SSES does does not not Ground water in Ground water in the the SSES SSES vicinity vicinity waswas involve involve thethe release release of of radioactive radioactive sampled monthly sampled monthly at at 2 2 indicator indicator material to material to ground ground waterwater directly directly oror locations (2S2 locations (2S2 andand 4S4) 4S4) and and one one control control indirectly through indirectly through the the ground.
ground. As As aa location (12F3) location (12F3) during during 2004.
2004.
result, there result, there are no effluent are no effluent monitoring monitoring data to data to compare compare with with REMP REMP ground ground With With thethe exception exception of of location location 4S4, 4S4, water monitoring water monitoring results.results. Ground Ground water water untreated ground untreated ground water water was was sampled.
sampled.
could conceivably could conceivably become become .. "" Untreated means Untreated means that the water that the water has has notnot contaminated by contaminated by leakage leakage or or spills spills from from undergone any undergone any processing processing such such a"s a"s the plant the plant or or byby the the washout washout or or filtration. chlorination.
filtration. chlorination. or or softening.
softening. At At deposition of deposition of radioactive radioactive material material that:
that: location 4S4, location 4S4, thethe SSES SSES Training Training Center, Center, might be might be airborne.
airborne. If deposited on If deposited on the the well water well water actually actually isis obtained obtained from from on- on-ground, precipitation/soi]
ground, precipitation/soi] moisturemoisture site and site and piped piped to to the the Training Training Center Center could aid in could aid in the the movement movement of of after treatment.
after treatment. This This 'sampling
'sampling is is radioactive materials radioactive materials through through thethe perfoimed as perfoimed as aa check check to to ensure ensure that that ground to ground to water water thatthat could could conceivably conceivably water has water has not not been been ni.dioactively ni.dioactively be pumped be pumped fofdrinking fofdrinking purposes.
purposes. No No contaminated. Sampling contaminated. Sampling is is performed performed at at use of use of ground ground water water forfor irrigation irrigation near near the Training the Training Center Center to to facilitate facilitate the the the SSES the SSES has has been been identified.
identified. sample collection sample collection process.
process.
Because routine SSES Because routine SSES operation operation Sample Preservation &
Sample Preservation &
releases primarily releases primarily tritium and, to tritium and, to aa lesser extent, lesser extent, isotopes isotopes of of xenon xenon andand Analysis Analysis krypton to krypton to the the air, air, no no radionuclides radionuclides attributable to attributable to SSES SSES operation operation areare Ground Ground waterwater samples samples were were analyzed analyzed expected to expected to bebe observed observed in in ground ground for "gamma':'emitting for "gamma':'emitting radionuc1ide radionuc1ide and and water. Iodine water. Iodine and and particulate particulate releases releases to to tritium activities.
tritium activities. Gamma Gamma spectrometric spectrometric the air the air are are negligible.
negligible. Gaseous Gaseous xenon xenon ana1yses of ana1yses of ground ground water water began began inin '1979
'1979 and krypton and krypton tend tend to to remain remain airborne; airborne; and tritium and tritium analyses analyses in in 1972; both prior 1972; both prior deposition or deposition or washout washout of of these these would would be be to SSES to SSES operation.
operation.
expected to expected to be be very very minimal.
minimal. Tritium Tritium would be would be the the most most likely likely radionuclide radionuclide to to the ground reach the reach ground with with precipitation precipitation and,and, if not if not lost lost toto streams streams (surface (surface water) water) by by runoff, move runoff, move readily through the readily through the soil soil to to the ground the ground water.
water.
2004 Radiological 2004 Radiological Environmental Environmental Monitoring Monitoring ReportReport 43 43
Grollnd Water Monitoring Monitoring Results Monitoring Results ,, The 2004 mean The 2004 mean tritium tritium activity activity levels levels for indicator for indicator and and control control monitoring monitoring locations were locations were 4949 pCill pCill and 20 pCi/l, and 20 pCi/l, Tritium activity levels Tritium activity levels in in ground ground waterwater respectively. Both respectively. Both thethe 2004 2004 indicator indicator
\\
~'
have typically have typically been been observed observed to to be be and control and control mean mean tritium tritium activity activity levels levels than in lower than lower in surface surface water. water. A A are within are within the the range range of of the the noticeable decline noticeable decline occurred occurred between between corresponding averages corresponding averages of of annual annual mean mean 1992 and 1992 and 1993. 1993. Fewer Fewer measurements measurements for prior for prior operational operational years. years. The The 2004 2004 were above were above the the analysis analysis sensitivities sensitivities in in mean tritium indicator mean indicator tritium activity activity isis lower lower 1993 than 1993 than in in 1992. 1992. than the than the corresponding corresponding range range for for preoperational years. preoperational years. The The 2004 2004 control control Gamma-emitting Gamma-emitting radionucHdesradionucHdes in in mean is mean is also also below below the the range range ofof the the excess of excess MDCs have of MDCs have beenbeen found found in in corresponding means corresponding means forfor preoperational preoperational only aa few only few samples samples in in all all the the years years that that years. years. these analyses these analyses have have been been performed. performed. The naturally The naturally occurring occurring radionuclides radionuclides All other All other nuclides nuclides werewere less less than than the the potassium-40 and potassium-40 and thorium-228 thorium-228 have have MDC. MDC. No No radioactivity radioactivity contributions contributions to to been measured been measured above above theirtheir MDCs MDCs ground water ground water from from thethe SSES SSES werewere occasionally in occasionally in ground ground water.water. identifiable in identifiable in 2004. 2004. Potassium-40 was Potassium-40 was reported reported in in 1979, 1979, 1981.1985, 1991,1992. 1981.1985, 1991,1992. 1993, 1993, and and 1997. Thorium-228 1997. Thorium-228 was was found found in in 1985 1985 and 1986. and 1986. The The man-made man-made radionuclide radionuclide cesium-137 has cesium-137 has been been detected detected only only occasionally since occasionally since 1979. 1979. Its'Its' presence presence has always has always beenbeen attributed attributed to to residual residual from previous fallout from fallout previous atmospheric atmospheric nuclear weapons nuclear weapons tests. tests. Results for Results for the the 2004 2004 specific specific ground ground water sample analyses water sample analyses may may be be found found inin Table 1-7 Table 1-7 of of Appendix Appendix I. I. AA summary summary of of the 2004 the 2004 ground ground waterwater monitoring monitoring data data may be may be located located in in Appendix Appendix G. G. Comparisons of Comparisons of 2004 2004 monitoring monitoring results for results for tritium tritium withwith those those of of past past years may years may be be found found in in Table Table H H 2020 of of Appendix H. Appendix H. During During 2004 2004 ,, tritium tritium was was measured measured above MDC above MDC in in one one sample sample at at control control location 12F3 location 12F3 at at aa concentration concentration of of 128 128 pCin. The pCin. The activity activity was was slightly slightly above above the detection the detection limit. limit. The The 20042004 indicator indicator values ranged values ranged fromfrom -44.3
-44.3 to to 123 123 pC/],
pC/], compared to compared to -67.4
-67.4 to to 193 193 pC/l pC/l forfor 2003.
2003.
\.J 44 44 20M Radiological 20M Radiological Environmental Environmental Monitoring Monitoring Report Report
References References 1.
- 1. Pennsylvania Power and Pennsylvania Power and Light Light Company, Company, "Susquehanna "Susquehanna Steam Steam Electric Electric Station, Station, Environmental Report, Environmental Report, Operating License Stage,"
Operating License Stage," May May 1978. 1978. 2.
- 2. Pennsylvania Power Pennsylvania Power and and Light Light Company, Company, "Susquehanna "Susquehanna Steam Steam Electric Electric Station, Station, Final Safety Analysis Final Safety Analysis Report".
Report". 3.
- 3. United States Nuclear United States Nuclear Regulatory Regulatory Commission, Commission, Office of Nuclear Office of Nuclear Reactor Reactor Regulation, "Final Regulation, "Final Environmental Environmental Statement Statement Related Related toto the the Operation Operation ofof Susquehanna Steam Susquehanna Steam Electric Electric Station, Station, Units Units 11 and and 2,"
2," Docket Docket Nos. Nos. 50-387 50-387 andand 50-388, June 50-388, June 1981. 1981. 4.
- 4. United States Nuclear United States Nuclear Regulatory Regulatory Commission, Commission, "An "An Acceptable Acceptable Radiological Radiological Environmental Monitoring Environmental Program," Radiological Monitoring Program," Radiological A~sessment Branch Branch Technical Technical Position, November Position, November 1979, 1979, Revision Revision 1.1.
5.
- 5. National Council on National Council on Radiation Radiation Protection Protection and and Measurements, Measurements, "Environmental "Environmental Radiation Measurement,"
Radiation Measurement," NCRP NCRP Report Report No. No. 50, 50, Washington, Washington, D.C., D.C., December 27, December 27, 1976. 1976. 6.
- 6. Oakley, D.C., "Natural Oakley, D.C., "Natural Radiation Radiation Exposure Exposure in in the the United United States,"
States," ORP/SID ORP/SID 72-172-1 Office of Office of Radiation Radiation Programs, Programs, U.S. U.S. Environmental Environmental Protection Protection Agency, Agency, Washington, D.C., Washington, D.C., June June 1972. 1972. 7.
- 7. Denham, D.H., Roberts, Denham, D.H., Roberts, M.C.,
M.C., Novitsky, Novitsky, W.M., W.M., Testa, Testa, E.D., E.D., "Investigation "Investigation ofof Elevated Cesium-137 Elevated Cesium-137 Concentrations Concentrations inin Small Small Game Game inin Luzerne Luzerne County, County, Pennsylvania:' Proceedings Pennsylvania:' Proceedings of of Papers Papers presented presented atat Health Health Physics Physics Society Society Tenth Tenth Midyear Topical Midyear Topical Symposium, Symposium, October October 11-13, 11-13, 1976, 1976, pgs. pgs. 271-279. 271-279. 8.
- 8. Currie L.A., uLower.Limit Currie L.A., uLower.Limit of of Detection:
Detection: Definition Definition and and Elaboration Elaboration ofof aa Proposed Proposed Position for Position for Radiological Radiological Effluent Effluent and Environmental Measurements," and Environmental Measurements," September 1984. NUREG/CR-4007, September NUREG/CR-4007, 1984. 9.
- 9. PPL, "Susquehanna PPL, "Susquehanna Steam Steam Electric Electric Station, Station, 2003 2003 Annual Annual Radiological Radiological Environmental Operating Report,"
Environmental Operating Report," April April 2004 2004 .. 10.
- 10. PPL, "Susquehanna Steam PPL, "Susquehanna Steam Electric Electric Station, Station, Radioactive Radioactive Effluent Effluent Release Release Report,"
Report," Data Period: Data Period: January January -- December December 2004 2004 ,, April April 2004. 2004.
- 11. m, "Susquehanna Ecology m,
- 11. Ecology "Susquehanna Steam Steam Electric Electric Station.
Station. 2004 2004 Land Land Use Use Census," Census," November 2004 November 2004 ..
- 12. PPL,
- 12. "Engineering Study, PPL, "Engineering Study, EC-ENVR-I012 EC-ENVR-I012 (Revision (Revision 0,0, January January 1995),"
1995)," Interpretation of Interpretation of Environmental Environmental TLDTLD Results. Results. 20~ Radiological ERl'ironmental Radiological ERl'ironmental Monitoring Monitoring Report Report .4S
.4S
APPENDIX A APPENDIX A \.."",-,.1 2004 Radiological 2004 Radiological Environmental Environmental Monitoring Monitoring Report Report A-I A-I
Appendix A Appendix A
,REIVIP Sample
,REIVIP Sample Collection; Collection; Analyses Analyses and and Methods Methods
\.J \.J An independent An independent consulting consulting gtoup, Ecology m, working gtoup, Ecology working at at Susquehanna's Susquehanna's Environmental' Environmental' Laboratory~ which which is is located located approximately approximately % miles miles east east of of the the SSES, SSES, collects collects and and processes samples. processes samples. Samples Samples are are brought'to brought'to the the laboratory, laboratory, stored, and shipped stored, and shipped to to two two
;; outside outside independent independent analytical analytical laboratories.
laboratories. The The foHowing foHowing table table summarizes summarizes the the REMP REMP sample 'collectioruanalyses sample 'collectioruanalyses by by independent' independent' laboratories laboratories during 2004. Note during 2004. Note that that TBE TBE
,represents'Teledyne Brown
,represents'Teledyne Brown Engineering, Engineering, E-LAB E-LAB represents represents Framatome Framatome ANP ANP and and E-ID E-ID represents Ecology represents Ecology ill, ill, Inc.
Inc. :: SOURCE SOURCE OF OF REl\1P REl\1P DATADATA FOR FOR MONITORING MONITORING YEAR YEAR 20042004
,Sample
,Sample Analysis Analysis Analysis :
Analysis Collection Collection Analytical Analytical Medium Frequency_ Procedure Number Number Procedure Procedure Number Number Medium .. Frequency_ Procedure Ambient Ambient "" TID TID Quarterly I Quarterly SSES, HP-TP-205 SSES, HP-TP-205 SSES,HP-TP-159 & SSES,HP-TP-159 & Radiation Radiation ; :190
- 190
'Air
'Air Gross Gross Beta Beta Wee~y E-ID, Appendix E-ID, Appendix 22 TBE-200S Gross TBE-200S Gross Alpha and/or Alpha and/or Beta Beta Activity in Activity in Various Various Matrices Matrices Air: 1-131 Weekly E-ID, AppendixAppendix 22 TBE-2012 Air: 1-131 Weekly E-ID, TBE-2012 Radioiodine in Radioiodine in
-- Various Various Matrices Matrices Air Air Gamma Gamma Quarterly Quarterly E-ID, Appendix E-ID, Appendix 22 "" TBE-2oo7 TBE-2oo7 GammaGamma Emit~ing Radioisotope Radioisotope Analysis Analysis Surface Surface Gross Beta Gross Beta Monthly Monthly E-ill, Appendix E-ill, Appendix 3, 3, 4, 4, TBE-200S Gross TBE-200S Gross Water Water ,, ,,
6,&7 6,&7 Alpha ~nd/or Beta Alpha Beta Activity in Activity in V~~us Matrices:
,, :: \\ tt .~"
Matrices: Drin~ng ,, Gross Gross Beta Beta Monthly Monthly ,,
,, E-ID, E-ID, AppendixAppendix 55 TBE-2008Gross TBE-2008Gross Water..
Water '&Gross
'&Gross Alpha and/or Alpha and/or Beta Beta
-- yin Various,
,Activityin Various, Alpha Alpha -- ,, '.'.""
,Activit
,, Matrices
** 'j
' j **
Matrices All Waters All Waters Tritium Tritium Monthly Monthly :: E':ID. E':ID. Appendix Appendix 3,4, 3,4, TBE-2010 Tritium TBE-2010 Tritium 5,6,7& 8 5,6,7& 8 and Carbon-14 and Carbon-14
f f ':':
.. Analysis by Analysis by Liquid Liquid
, \
, \! ! ,,
'Scintillation'
'Scintillation' Surface Surface &. &. Gamma Gamma Monthly Monthly ::
E-ill, Appendix E-ill, Appendix 3,4, 3,4, E-LAB-305 "" ,, E-LAB-305 Drinking Drinking 5,6, & 5,6, & 77 Preparation of Preparation of Water Water .. Environmental and Environmental and Bioassay Media Bioassay Media for for Ana1ysis of Ana1ysis of Gamma Gamma Ray Emitters Ray Emitters 2004 Radiological 2004 Radiological Environmental Environmental MC?nit.o.~ing Rep0l:1,_ Rep0l:1,_ A*2
Appendix A Appendix A Sample Sample Analysis Analysis Analysis Analysis Collection Collection Analytical Analytical Medium Medium -- Frequency Frequency Procedure Number Procedure Number Procedure Number Procedure Number Ground Ground Gamma Gamma Monthly* E-ill, Appendix. E-ill, Appendix. 88 E-LAB-305 E-LAB-305 Water Water .. Preparation Preparation of of
.. Environmental Environmental and and Bioassay Media Bioassay Media for for
.. Analysis Analysis of of Gamma Gamma Ray Emitters.
Ray Emitters. Surface Surface && 1-131 1-131 Monthly Monthly E-ill, Appendix. E-ill, Appendix. 4, 4, 5, 5, E-LAB-340 E-LAB-340 Drinking Drinking 6, and 6, and 77 Detennination of Detennination of Water Water Iodine-131 in Iodine-131 in ,, Environmental Media Environmental Media Using Anion Using Anion '.'.
~change Chromatography Chromatography .. Milk Milk Gamma Gamma Monthlyl E-ill, Appendix E-ill, Appendix 99 E-LAB-305 E-LAB-305 Semi-Monthly Semi-Monthly Preparation of Preparation of Environmental and Environmental and Bioassay Media Bioassay Media for*
Analysis Analysis ofof Gamma Gamma Ray Emitters Ray Emitters Milk Milk 1-131 1-131 Monthlyl E-ill, Appendix E-ill, Appendix 99 E-LAB-340 E-LAB-340 Semi-Monthly Semi-Monthly Determination of Determination of Iodine-131 in Iodine-131 in Environmental Media Environmental Media Using Anion Using Anion Exchange Exchange Chromatography Chromatography Fish Fish Gamma Gamma Semi-Annually Semi-Annually E-ill, Appendix. E-ill, 11 Appendix. 11 TBE-2007 gamma TBE-2007 gamma
..(SpringlFall)
(SpringlFall) Emitting Emitting Radioisotope' Radioisotope' Analysis Analysis Sediment Sediment Gamma Gamma Semi-Annually Semi-Annually E-ill, Appendix E-ill, Appendix 1212 TBE-2007 gamma TBE-2007 gamma (SpringlFaU) (SpringlFaU) Emitting Emitting Radioisotope Radioisotope Analysis Analysis Fruits Fruits && Gamma Gamma In Season In Season E-m, Appendix E-m, Appendix 1313 TBE-2007 gamma TBE-2007 gamma Vegetables Vegetables (when irrigated) (when irrigated) Emitting Emitting Radioisotope Radioisotope Analysis Analysis A*3 2004 Radiological 2004 Radiological Environmental Environmental Monitoring Monitoring Report Report
Appendix A Appendix A Sample Sample Analysis Analysis Analysis Analysis Collection Collection Analytical Analytical l\'Iedium l\'Iedium ..
.. II ***.
***. 'FrequenCY;
'FrequenCY; Number
'Procedure Number
'Procedure Procedure Nuniber Procedure Nuniber Soil Soil Gamma Gamma Annually Annually E-ID, Appendix E-ID, Appendix 14 14 E*LAB-30S of, Pn!paration of, Pn!paration Environmental and Environmental and Bioassay Media Bioassay Media for for of Gamma Analysis of Analysis Gamma Ray Emitters Ray Emitters
,I
,I (( L.
L. PROGRAl\1 CHANGES: PROGRAl\1 CHANGES: Direct Radiation Direct Radiation Monitoring Monitoring Eighty-four Eighty-four TLD TLD monitoring monitoring locationslocations were were utiUzed utiUzed for for direct direct radiation radiation measurements' measurements' .. during 2003. during 2003. A A reduction reduction of of twenty-six twenty-six TLDs TLDs in in the the field field was was implemented implemented 102004. 102004. 'As
'As aa result fifty-eight result fifty-eight TLDs TLDs were were utilized utilized in in the the field field for for direct direct radiation radiation monitoring monitoring inin 2004.
2004. The elimination The ofTLDs was elimination ofTLDs was due due to to the'proximity the'proximity of of other other TLD TLD monitoring monitoring locations locations to to the deleted the deleted sites sites and and the the range range of of distances distances from from the the SSES SSES at at which which some some of ofthe' the' TLDs are TLDs are located. The located. The extra extra 26 26 TLD TLD locations locations did did not not provide provide additional additional benefit benefit and and were were deleted, deleted, from the from the monitoring monitoring progra~ in in 2004. 2004. Air Monitoring Air Monitoring ,, There There were were no no changes changes toto the the air air monitoring monitoring program program during 2004. during 2004. Surface 'Vater Surface 'Vater andand Drinking Drinking Water Water Monitoring Monitoring 1n 2004lhe frequency 1n 2004lhe frequency ofl-131 ofl-131 analysis analysis for for surface surface and and drinking drinking water water samples samples was was revised from revised from bi-weekly bi-weekly toto monthly monthly (on (on aa two two weekweek composite composite sample). sample). The The monitoring monitoring .. locations affected locations affected byby this this change change are are as as follows: follows: Locations: Locations:
Description:
Description:
6S6 6S6 River Water River Water IntakeIntake Line Line 2S7/6S7 2S7/6S7 Cooling TowerBIowdown Cooling TowerBIowdown Discharge Discharge 6SS 6SS Outfall Area Outfall Area 12H2 12H2 Danville Water Danville Water Authority Authority Additionally, performance Additionally, performance of of monthly monthly 1-131 1-131 analysisanalysis on on LTAW LTAW samples samples has has been been deleted. deleted. l\1i1k l\lonitoring l\1i1k l\lonitoring There were There were no no changes changes toto the the milk-monitoring milk-monitoring program program in in 2004 2004 .. 2004 Radiological 2004 Radiological Environmental Environmental Monitoring Monitoring Report Report II '....
.! II
II Appendix A Appendix A Ground Water Ground Water Monitoring Monitoring There were There were no no changes changes to to the the ground ground water water monitoring monitoring program program during during 2004 2004 .. Fruits & Fruits & Vegetables Vegetables There were There were no no changes changes to to the the fruits fruits and and vegetable vegetable program program during during 2004 2004.. .. Soil Soil Monitoring Monitoring There were There were no no changes changes to to the the soil soil monitoring monitoring program program in in 2004. 2004. Sediment 1\fonitoring Sediment 1\fonitoring There were There were no no changes changes to to the the sediment sediment monitoring monitoring program program in in 2004. 2004. Fish Monitoring Fish Monitoring There were There were no no changes changes to to the the fish fish monitoring monitoring program program in in 2004. 2004. A-S A-S 2004 Radiological 2004 Radiological Environmental Environmental Monitoring Monitoring Report Report
Appendix A Appendix A PROGRAM EXCEPTIONS PROGRAM EXCEPTIONS Exceptions are Exceptions are listed listed below: below: 1.
- 1. Suiface water Suiface water 1-131 1-131 low low level level results results for for locations locations 2S72S7 (Cooling (Cooling Tower:
Tower: Blowdown discharge). 6S5 Blowdown discharge). 6S5 (River (River sample), sample), and and 6S6 6S6 (River (River Water Water Intake) Intake) were were unacceptable for unacceptable for the the following following samples:samples:
*04/06/2004 -- 0412012004 6S6 Unable 6S6 Unable to to achieve achieve MOCMOC level level due due to to low low chemical chemical yield yield
*04/06/2004..:04/20/2004 .. *2S7 Unable Unable to to achieve MOC level achieve MOC level due due to to low low chemical chemical yield yield
*04/06/2004 -- 04/20/2004 6S5 6S5 Unable Unable to.achieve to.achieve MOC MOC levellevel due due to to low low
'ch~mic'al yield yield
** Required Required MOC's MOC's werewere not not met:'Prariultonecorrective met:'Prariultonecorrective action action #CR04-09
#CR04-09 initiated initiated to investigate to investigate cause.
cause. The The affected affected analysis analysis results results were were notnot incorporated incorporated into into Appendix Appendix I, I, Table Table G. G. .. rr "" 2.
- 2. Surface water auto Surface water auto composite composite sampler sampler at at location location 2S72S7 (( Cooling Cooling Tower Tower Blowdown discharge)
Blowdown discharge) waswas out out of of service service during during the the following following periods: periods: 08110/2004 -- 0811712004 due due to to electronics electronics failure failure Corrective Action: Corrective Action: Samples Samples were were taken taken from from the the backup backup composite composite sampler sampler location 6S7.* ,, .. location 3.
- 3. Surface water auto Surface water auto composite composite sampler sampler at at location location 6S6 6S6 (River (River Intake)
Intake) was was out out of of service during service during the the fonowing fonowing periods: periods: 11130/2004 -12107/2004 due due to to blocked blocked sample sample line line caused caused by by debris debris from from high high river level.' river level.' \\ '. '. .. .. Corrective Action:*' Grab Corrective Grab sample sample was was ta~en at at alternate alternate location location 5S9. 5S9.
;". :, (( """" ii ;; ~ "" *.
.. 200~ Radiological Radiological Environmental Environmental Monitoring Monitoring Report Report A*6
Appendix A Appendix A 4.
- 4. Milk sample 1-131 Milk sample 1-131 low low level level results results for for locations locations II OD OD 1,1, 10D2 10D2 and and lOG lOG 1 1 could could riot riot be analyzed be analyzed byby the the laboratory laboratory forfor the the fonowing fonowing reasons:
reasons:
*06/20/2004- Location 10D2
*06/20/2004- Location 10D2 duedue to curdled milk to curdled milk unable unable to to be be analyzed analyzed
*08/02/2004 -- Location
*08/02/2004 Location lOG lOG 11 due due to to curdled curdled milk milk unable unable to to be be analyzed analyzed
*09/0112004 -- Location
*09/0112004 Location 10Dl10Dl andand IOD2 IOD2 due due to to curdled curdled milk milk unable unable toto be be analyzed analyzed
** The The affected affected milk milk analyses analyses were were not not incorporated incorporated intointo Appendix Appendix II or or G.G.
5.
- 5. TLD measurement TLD measurement results results for for locations 15A3, 12D2, locations 15A3, 12D2, and 16A2 could and 16A2 could not not be be analyzed analyzed forfor the the following following reasons:
reasons: nd 2 nd 2 Quarter 2004 Quarter 2004 -- 15A3 and 15A3 and 12D2 12D2 werewere lost lost in in the the field, field, no no data. data. rd rd Quarter 2004 3 Quarter 3 2004 -- 16A2 lost in 16A2 lost in the the field, field, no no data. data. 4th Quarter 4th Quarter 2004-2004- ID5 and ID5 IIEI were and IIEI were water water damaged, damaged, not not able able to to process. process. In 2004 In 2004 the the SSES SSES REMP performance was REMP ~verall performance was asas follows: follows: Sample Collection Sample Collection 850 of 850 of 850 850 samples samples were were collected. collected. Sample Analysis Sample Analysis .\...J
.\...J 1388 of 1388 of 1395 1395 analyses analyses were were performed performed on on 850 850 samples.
samples. TLD Direct TLD Direct Radiation Radiation Measurements Measurements 253 of258 253 of258 TLDTLD measurements measurements were were analyzed. analyzed. Each discrepancy was Each discrepancy was reviewed reviewed to to understand understand the the causes causes ofof the the program program exception. exception. Sampling analysis Sampling analysis deficiencies deficiencies were were reviewed reviewed withwith the the responsible responsible individuals individuals toto prevent prevent recurrence. Occasional recurrence. Occasional equipment equipment breakdowns breakdowns were were unavoidable. unavoidable. For 2004 the For 2004 the surface surface water automatic water automatic composite composite samples samples (2S7 (2S7 and and 6S6) 6S6) each each operated operated 358 of365 days 358 of365 days ofthe ofthe year at year at 98% 98% operability. operability. All All other other sampling sampling equipment equipment operated operated without without any any breakdowns breakdowns for 100% for 100% of of the the year. year. .\-7 .\-7 2004 Radiological 2004 Radiological Environmental Environmental Monitoring Monitoring Report Report
APPENDIXB APPENDIXB 2004 Radiological 2004 Radiological Environmental Environmental Monitoring Monitoring Report Report B*l
AppendixB TABLEt TABLEt (page 11 of (page of 2) 2)
- Annual Annual Analy"tical Analy"tical Schedule Schedule for for the the PPL Susquehanna PPL Susquehanna Steam Steam Electric Electric Station Station Radiological Enyironmental Radiological Enyironmental Monitoring Monitoring Program Program -- 2004 2004 No. of No. of Sample "';
Sample "'; Analysis Analysis Media & Media Code
& Code Locations Locations Freq.(a)
Freq.(a) Analyses Required Analyses Required Freg. (b) Freg. (b)
,, !! tt '"
Airborne Airborne 6 6 W W ,I
, I !;
!; ,Gross Beta
,Gross Beta (c)
(c) W W Particulates Particulates '.¥.
'.¥. Gamma Gamma Spectrometry, Spectrometry, QC QC ,, Airborne Airborne Iodine Iodine 6 6 W W I-J31 I-J31 W W
JJ :: ;.
.'Gamma
.'Gamma Spectrometry Spectrometry
** ,~l' Sediment Sediment 4 4 SA SA SA SA
~' ~ .'. .'. i' i' .! .!
Fish Fish 2 2 SA .:.:
SA ,'",
'Gamma Spectrometry
'Gamma Spectrometry SA SA 1
1 A .... ** A ,'.
,'. (on edible (on edible portion) portion) A A
Surface Water Surface Water (d) (d) 5 5 WforMC WforMC
,Gross Beta
,Gross Beta M M
,, '-.'-. Gamma Gamma Spectroscopy Spectroscopy M M
i. i.
'Tritium
'Tritium M M
WforBWC, I~131 (once WforBWC, (once per per month) month) M M Well (ground) Well (ground) 3 3 M M Gamma Spectroscopy Gamma Spectroscopy M M Water Water Tritium Tritium M M \.J \.J ,, .. ** ** ~! ,, Drinking Water: Drinking Water: (e) (e) 1 1 WfoiMC WfoiMC Gross Alpha Gross Alpha M M
;; ~ ~: ,, .... ,Gross Beta
,Gross Beta M M
... Gamma Spectrometry Gamma Spectrometry M M
Tritium Tritium M M W for,BWC W for,BWC '-I-131,(once '-I-131,(once per month) per month) M M Cow Milk Milk 4(f) 4(f) 1-131 SM,M Cow M,swl" 1-131 Gamma Spectrometry Spectrometry SM,M SM,M
.... .... Gamma SM,M Food Products (g)
Food Products (g) 1 1 A A "" ~ ~ ** jj '.,'
'.,' ;; rr J J '-l
'-l '.'
'.' Gamma Gamma Spectrometry Spectrometry A A
(potatoes) (potatoes) Soil Soil 4 4 A A Gamma Spectrometry Gamma Spectrometry A A Direct Radiation Direct Radiation 58 58 Q Q TLD TLD Q Q 2004 Radiological 2004 Radiological Environmental Environmental Monitoring Monitoring Report Report B-2 B-2
Appendix B Appendix B (a). (a). W =
= weekly. BW W weekly. =
=
BW bi-weeklybi-weekly (once (once per per month), month), BWC =
=
BWC bi-weekly bi-weekly composite, composite, M M
=
= monthly, SM monthly, =
=
SM semi-monthly, semi-monthly, Q =
=
Q quarterly, quarterly, QC =
=
QC quarterly quarterly composite, composite, SA SA =
=
semi-annualIy, semi-annualIy, A =
=
A annually, annually, MC =
=
MC monthly monthly composite. composite. (b) (b) Codes are Codes are the the same same as as for for sample sample frequency. frequency. ,, (c) (c) If the gross If the gross beta beta activity activity were were greater greater than than 10 10 times times the yearly mean the yearly mean ofof the the control control sample, gamma sample, gamma analysis analysis wouldwould be be perfonned perfonned on on the the individual individual filter. filter. Gross Gross beta beta analysis was analysis was perfonned perfonned 24 24 hours hours oror more more fonowing fonowing filter filter change change to to anow anow forfor radon and radon and thorium thorium daughter daughter decay. decay. (d) (d) Locations Locations 6S6,6S6, 6S7, 6S7, and2S7and2S7 are are automatic automatic composite composite samplers samplers suchsuch that that ti~e proportional sampling proportional sampling was was perfonned perfonned at at these these locations locations the the entire entire year. year. Samples Samples are collected are collected weekly weekly for for bi-weekly bi-weekly composite composite andand monthly monthly composite composite samples. samples. Location 6S5 Location 6S5 isis aa sample sample from from thethe Susquehanna Susquehanna RiverRiver location location downriver downriver of of the the SSES discharge SSES discharge diffuser. diffuser. Station Station 6S5 was grab 6S5 was grab sampled sampled weekly. weekly. An An alternate alternate shoreline site shoreline site located located below below the the SSES SSES discharge discharge diffuser diffuser is is used used when when river river conditions prohibit conditions prohibit boating. boating. TheThe shoreline shoreline samples samples are are collected collected atat the the Wetlands Wetlands Cottage area, Cottage area, approximately approximately 100-150 100-150 years years downriver downriver from from thethe 6S5 site. LTAW 6S5 site. LTAW was grab was grab sampled sampled monthly. monthly. (e) (e) Water from location Water from location 12H2 12H2 waswas retrieved retrieved weekly. weekly. Composite Composite samplessamples of of the the weekly collections weekly collections at at this this location location were were made made both both monthly monthly (MC) (MC) andand biweekly biweekly (BWC) for (BWC) for analysis. analysis. Sampling Sampling at at 12H2 12H2 was was perfonned perfonned using using anan automatic automatic composite sampler composite sampler (ACS) (ACS) thatthat was was operated operated in in the the time-proportional time-proportional mode. mode. (f) (f) Locations 10D!, IOD2, Locations 10D!, IOD2, 10GI, 10GI, and and 12B2 12B2 were were sampled sampled semi-monthly semi-monthly from from April April through October through October whenwhen cows cows are are onon pasture, pasture, monthly monthly otherwise. otherwise. (g) (g) Location (12F7) briefly Location (12F7) briefly irrigated irrigated potatoes potatoes in in June June 2004 2004 using using Susquehanna Susquehanna RiverRiver water (no water (no other other fields fields within within 1010 miles miles downriver downriver of of Susquehanna Susquehanna SES SES were were irrigated in irrigated in 2004. 2004. B-3 B-3 2004 Radiological 2004 Radiological Environmental Monitoring Report Environmental Monitoring Report
APPENDIXC APPENDIXC 2004 Radiological 2004 Radiological Enl'iromnental Enl'iromnental Monitoring Monitoring Report Report C-l C-l
--- .. _._. ~
AppendixC AppendixC TABLECI TABLECI (page 1 (page 1 of of 5) 5) TLD Locations for TLD Locations for the the SSES SSES Radiological Environmental Radiological Environmental MonitoringMonitoring Program Program -- 20042004 Less Than Less Than One One Mile Mile from from the the SSES{a) SSES{a) .... See See Figure Figure 22 Location Location Distance Distance Direction Direction Description Description Code(a) Code(a) (miles) (miles) IS2 IS2 0.2 0.2 N N Perimeter Fence Perimeter Fence 2S2 0.9 0.9 NNE NNE Energy Infonnation Energy Infonnation Center Center 2S3 2S3 0.2 0.2 NNE; NNE; Perimeter Fence Perimeter Fence 3S2 3S2 0.5 0.5 NE NE SSES Backup SSES Backup Met Met Tower Tower 3S3. 3S3. 0.9 .. 0.9 NE NE ANSP Riverlands ANSP Riverlands Garden Garden
.... .4S3
.4S3 0.2 0.2 ENE ENE Post, West Post, West of of SSES SSES APF APF
4S6 0.7 0.7 ENE ENE Riverlands Riverlands 5S4 ".". 5S4 O.S O.S E* West of West of Environmental Environmental Laboratory Laboratory 5S7 '.'. 5S7 0.3 0.3 E E Perimeter Fence Perimeter Fence 6S4 6S4 0.2 0.2 ESE ESE ..Perimeter Perimeter Fence Fence (north) (north) 6S9 6S9 .-.- 0.2 0.2 ESE ESE Perimeter Fence Perimeter Fence (south) (south) 7S6 7S6 0.2 0.2 SE SE Perimeter Fence' Perimeter Fence' 7S7 7S7 0.4 0.4 SE SE End of End of Kline's Kline's Road Road SS2 SS2 0.2 0.2 SSE SSE Perimeter Fence Perimeter Fence 9S2 9S2 0.2 0.2 S S Security Fence Security Fence 10S1 10S1 0.4 0.4 SSW SSW Post -- south Post south of of switching switching station station 10S2 10S2 0.2 0.2 SSW SSW Security Fence Security Fence 11S3 11S3 0.3 0.3 SW SW SecurityFence SecurityFence 11S7 11S7 0.4 0.4 .SW
.SW SSES Access SSES Access Road Road Gate Gate #50
#50 12S1 12S1 0.4 0.4 WSW WSW SSES West SSES West Building Building 2004 Radiological 2004 Radiological Environmental Environmental Monitoring Monitoring Report Report C-2 C-2
AppendixC AppendixC TABLECI TABLECI (Page2ofS) (Page2ofS) TLD Locations for TLD Locations for the the SSES SSES Radiological Environmental Radiological Environmental Monitoring Monitoring Program Program -- 2004 2004 Less Than Less Than One One Mile Mile from from the the SSES(a) SSES(a) -- See See Figure Figure 22 Location Location Distance Distance Direction Direction Description Description Code (a) Code (a) (miles) (miles) 12S3 12S3 0.4 0.4 WSW WSW Perimeter Fence Perimeter Fence 13S2 13S2 0.4 0.4 W W Perimeter Fence Perimeter Fence 13SS 13SS 0.4 0.4 W W Perimeter Fence Perimeter Fence 13S6 13S6 0.4 0.4 W W Fonner Laydown Fonner Area -- west Laydown Area west of of Confer's Confer's Lane Lane 14SS 14SS O.S O.S WNW WNW Beach Grove Beach Grove Road/Confer's Road/Confer's Lane Lane ISS5 ISS5 0.4 0.4 .. NW NW Perimeter Fence Perimeter Fence 16S1 16S1 0.3 0.3 ~(east) .... .. -- 16S2 16S2 0.3 0.3 (west) (west) 6A4* 6A4* 0.6 0.6 ESE ESE Restaurant (U.S. Restaurant (U.S. Route 11) Route 11) SA3 SA3 0.9 0.9 SSE SSE PPL Wetlands PPL Wetlands Sign Sign (U. S. Route (U. S. Route 11) 11) ISA3* ISA3* 0.9 0.9 NW NW Hosler Residence Hosler Residence 16A2* 16A2* O.S O.S NNW NNW Benkinney Residence Benkinney Residence C-3 C-3 2004 Radiological 2004 Radiological Environmental Environmental Monitoring Monitoring Report Report
AppendixC AppendixC TABLECI TABLECI (page 33 of5) (page of5) TLD Locations for TLD Locations for the the SSES SSES Radiological Environmental Radiological Environmental Monitoring Monitoring Program Program -- 2004 2004 From One From One toto Five Five Miles Miles from from the the SSES(a) See Fi~re 33 SSES(a) -- See Location Location Distance Distance Direction Direction Description Description Code (a) Code (a) (miles) (miles) 8B2* .. 8B2* 1.4 1.4 .. SSE SSE Lawal1 Residence Lawal1 Residence 9Bl 9Bl 1.3 1.3 S S Transmission Line Transmission Line -- east east of of Route Route 11 11 10B3* 10B3* 1.7 1.7 SSW SSW Casteklnc. Casteklnc. 105 105 4.0 4.0 *N .... ShickshinnylMocanaqua Sewage ShickshinnylMocanaqua Sewage Treatment Treatment PIt. PIt. 803 803 4.0 4.0 SSE SSE MowI)' Residence MowI)' Residence 904 3.6 3.6 S S Count!)' Folk Count!)' Folk Store Store 904 1001 1001 3.0 3.0 SSW SSW R. & R. & C. C. R}'!!!an R}'!!!an Fann Fann
~ ..
1202 1202 3.7 3.7 WSW. WSW. Dagostin Residence Dagostin Residence 14DI 14DI 3.6 3.6 .. WNW WNW HiUll\1ingle Inn Moore~s HiUll\1ingle Inn Roads Roads Intersection Intersection 3El 3El 4.7 4.7 NE NE Webb Residence Webb LUly Lake Residence -- LUly Lake 4E2 4E2 4.7 4.7 ENE ENE Ruckles HiIlIPond Ruckles HiIlIPond Hill Hill Roads Roads Intersection Intersection 5E2 5E2 4.5 4.5 E E BIossFann BIossFann 6El 6El 4.7 4.7 ESE ESE S1. James S1. James Church Church 7El 7El 4.2 4.2 SE SE Harwood Transmission Harwood Transmission LineLine Pole #2 Pole #2 lIEI lIEI 4.7 4.7 SW SW Thomas Residence Thomas Residence 12El 12El 4.7 4.7 WSW' WSW' Berwick Hospital Berwick Hospital 13E4 13E4 4.1 4.1 W W Kessler Farm Kessler Farm 12S7 12S7 1.1 1.1 WSW WSW Kisner Residence Kisner Residence 2004 Radiological 2004 Radiological Environmental Environmental Monitoring Monitoring Report Report C-4 C-4
Appendix CC TABLECI TABLECI (Page 44 of (Page of 5) 5) TLD Locations for TLD Locations for the the SSES SSES Radiological Environmental Radiological Environmental Monitoring Monitoring Program Program -- 2004 2004 Greater than Greater than Five Five I\tliles I\tliles from from the the SSES(a) SSES(a) -- See See Figure Figure 44 Location Location Distance Distance Direction Direction Description Description Code (a) Code (a) (miles) (miles) 2Fl 2Fl 5.9 5.9 NNE NNE St. Adalberts Cemetery St. Adalberts Cemetery 15Fl 15Fl 5.4 5.4 mv mv Zawatski Fann Zawatski Fann 16Fl 16Fl 7.8 7.8 NNW NNW Hidlay Residence Hidlay Residence ..~ 3G4** 3G4** 17 17 NE .. NE Wilkes Barre Wilkes Barre Service Service Center Center 4Gl** 4Gl** 14 .. 14 ENE ENE Mountaintop -- Crestwood Mountaintop Crestwood Industrial Industrial Park Park 7Gl** 7Gl** 14 14 SE SE Hazleton PP&L Hazleton PP&L Complex Complex 12Gl** 12Gl** 15 15 WSW WSW PPL Service PPL Service Center, Center, Bloomsburg Bloomsburg 12G4** 12G4** 10 10 WSW WSW Naus Residence Naus Residence
,, ii
"-..J c-s 2004 Radiological 2004 Radiological Environmental Environmental Monitoring Monitoring Report Report
Appendix C Appendix C TABLE'CI TABLE'CI (pageS ofS) (pageS ofS) TLD Locations for TLD Locations for the the SSESSSES Radiological Environmental Radiological Environmental Monitoring Monitoring Program Program -- 2004 2004 "" a) a) All distances from All distances from thethe SSES SSES to to monitoritig monitoritig lOCations lOCations are are measured measured from from the the ,, standby gas standby gas treatment treatment vent vent at at 442001N34 442001N34 1 117 17 (pa. (pa. Grid Grid System). System). TheThe location location codes are codes are based based onon both both distance distance and and direction direction fromfrom the the SSES. SSES. The The letters letters in in the the location codes location codes indicate indicate if if the the monitoring monitoring locations locations are are on on site site (within (within the the site site boundary) or, boundary) if they or, if they areare not not on on ~ite, the the approximate approximate distances distances of of the the locations locations from the from the SSES SSES as as described described below:below: on site S -- on S site E- 4-5 E- miles 4-5 miles A -- <I A 20miles H- >20miles D 4 D 4 miles miles ** -- Special Special interest interest areas areas
** -- Control
** Control TLDs TLDs The numbers The preceding the numbers preceding the letters letters iri the location iri the location codescodes provide provide thethe directions directions of, of, the monitoring locations the monitoring locations from from thethe SSES SSES by by indicating indicating the the sectors sectors inin which which they are they are 1ocated. A 1ocated. A total total of of 16 16 sectors sectors (numbered (numbered 11 through through 16) 16) equal1y equal1y divide divide an an ,,
imaginary circle imaginary circle onon aa map map of of the,SSES the,SSES and and its its :vicinity,
- vicinity, ~ith thethe SSES.
SSES. at at the the center center of the of the circle. circle. The The middle middle of of sector sector 11 is is directed directed due due north north (N). Moving clockwise (N). Moving clockwise from sector from sector 1,1, the the sector sector immediately immediately adjacent adjacent to to sector sector 11 is is sector sector 2,2, the the middle middle of of which is which is directed directed duedue norih, norih, northeast northeast ~). Continuing Continuing to to move move clockviise, clockviise, the the sector numbers sector numbers increase increase to to 16, 16, 'Yhich
'Yhich is is the the north, north, nort~west sector. sector.
.. :: Ii..
Ii.. '" The numbers following The numbers following the the lettersiit'the lettersiit'the location location codescodes are are used used to to differentiate differentiate sampling locations sampling locations found found in in the the same same sectorssectors at at approximately approximately the the same same distances distances from the from the SSES. SSES. 2004 Radiological 2004 Radiological Environmental Environmental Monitoring Monitoring Report Report C-6 C-6
Appelldix C Appelldix C TABLEC2 TABLEC2 (Page 11 of (Page of 4) 4) Sampling Sampling Locations Locations for for the the SSES SSES Radiological Environmental Radiological Environmental Monitoring Monitoring Program Program -:- -:- 2004 2004 Less Less Than Than One One :Mile :Mile from from the the SSES(a) SSES(a) -- See See Figure Figure 55 Location Location Code(a) Code(a) Distance Distance Direction Direction Description Description (miles) (miles)
- ~:. :;;:r:;:.,t ',L ;.i}',:*i~~,!~;>;.<*~;f: ,;'i,.':';~;::SURFACE~WA TER;-:;: L*t:::'!;~**::;,.~:: :!i: :!i: 1:,,',,;-~r;'.;'~:,:'~::;:Ft;"'> ,1,;" ;,' '7i 2S7 2S7 0.1 0.1 NNE NNE Cooling Cooling Tower Tower Blowdown Blowdown Line Line 6S5 6S5 0.9 0.9 ESE ESE Outfall Area Outfall Area 6S6 6S6 0.8 0.8 ESE
ESE River Water River Water Intake Intake Line Line 6S7 6S7 0.4 0.4 ESE ESE Cooling Tower Cooling Tower Blowdown Blowdown Line Line (alternate (alternate for 2S7) for 2S7)
LTAW LTAW 0.7 0.7 NE-ESE NE-ESE Lake Took-A-While Lake Took-A-While (on (on site) site) ,0, :;:::~\::~,:,':;~!t:,: .:
- 1:;;,',,:,. ,. c' ' : , ":\',~i~;:~~~:"~:~C' ::~, FISH(b}f.~~~* '.: ,:" ';: ';~;~;:::--.'. ,,'~1!:,,;if;.;~ ;':!J~*,,\!t.::.>' ]:';' :~ :;:t:"-5; LTAW LTAW 0.7 0.7 NE-ESE Lake NE-ESE Lake Took-A-While Took-A-While (on (on site) site)
';: ;;,~:'::: ~f:l'!r: ;;';; :';,".i~; 'f::';".": ~i: , :/', ,.::*>'SEDlMENT(cL:;'i:'~ ',';.\.': ::,,;;':;,'J(~'... ~.;"::~!;\';,;:'i:\:{;~(:'~,;. ;,.:~,.; LTAW LTAW 0.7 0.7 NE-ESE Lake NE-ESE Lake Took-A-WhiJe Took-A-WhiJe (on (on site) site)
;;:.!;~":~... _, -"~;~:~ ((',:: i'.::,~,~.;~:-~' ;:':':;:/:~~;~'; ;;;t~~.. , ,,~:"~::';: ,;~ '/i ;,>:~;AIR;~ .~~:::::;; :,~: :~:". ~ i' 0;;;.,::,,> ';.~W';:,~::':;*:'~*:'r~:'.'~ ,,;j~~.: ;-;;;-~ ~,,~~ :i; 3S2 3S2 0.5 0.5 NE NE SSES Backup Meteorological SSES Backup Meteorological Tower Tower .0 12S1 12S1 0.4 0.4 WSW WSW SSES West SSES West Building Building ""
13S6 13S6 0.4 0.4 'W
'W " Fonner Laydown Fonner Laydown Area, Area, West West of of Confers Confers Lane Lane
. . ._. . ;r ;I"~'~'"
':.' 1!_,~. __ .~~.:'",
* ~'_ -: '":, ;"':*r\,~r~,:-f';~~'::-~~*c'*
":"." -: ' . f -.'_ J.'- ***
SOII:.' ..*c.::.:;:,:,,:'.' SOII:. 'i"
. .~. ..,", :\\" ,:~. ~::, ',~t:.: :,.,:;,:"'~--,!~
J,,' * ,.-.'!;:--,
':.;: .t,:;'!;' ,',
":'" '" '~. -'., <.;,
"~*,:;;;;-l~;;t:~:;..:"'. :J:
3S2 3S2 0.5 0.5 NE NE SSES Backup Meteorological SSES Backup Meteorological Tower Tower 12S1 12S1 0.4 0.4 WSW WSW SSES West SSES West BuildingBuilding 13S6 13S6 0.4 0.4 W W Fonner Laydown Fonner Laydown Area, Area, West West of of Confers Confers Lane Lane C-7 C-7 2004 Radiological 2004 Radiological EnvironmentalEnvironmental Monitoring Monitoring Report Report
'" ff "" ..
C Appendix C Appendix TABLEC2 TABLEC2 (page 22 of (page of 4) 4) Sampling LoCations for Sampling LoCations for the the SSES SSES .. Radiolo Radiolo ical ical Environmental Monitorin Pro Environmental Monitorin Pro ram ram -- 2004 2004 Less Than Less Than One One Mile Mile from from the SSES(a}.. See the SSES(a}.. See FiFi re 55 re Distance Distance Direction Direction .. Description Description (miles) (miles) 2004 Radiological 2004 Radiological Environmental Environmental Monitoring Monitoring Report Report c-s c-s
Appendix C Appendix C TABLEC2. TABLEC2. (Page 3 (Page 3 of4) of4) Sampling Locations for Sampling Locations for the the SSES SSES Radiolo ical Environmental Radiolo ical Environmental Monitorin Monitorin Pro Pro ram ram -- 2004 2004 Greater than Greater than Five Five Miles Miles from from the SSES(a) ** See the SSES(a) See Fi Fi re 7 re 7 Direction Direction Description Description PPL SFC PPL SFC -- Humbolt Humbolt Industrial Industrial Park Park \.J
\.J 12F3 12F3 5.2 5.2 wsw wsw Berwick Water Berwick Water Com Com an an 2004 Radiological 2004 Radiological Environmental Environmental Monitoring Monitoring Report Report
:-:-:':-~----------------- .. .. '"
Appendix C Appendix C TABLEC2 TABLEC2 (Page 4 (Page 4 of4) of4) Sampling Sampling Locations Locations for for thethe SSES SSES Environmental Monitoring Radiolo~ical Environmental Monitoring Program Program -- 2004 2004 a) a) All distances from All distances from the the SSES SSES to to monitoring monitoring locations locations areare measured measured from from thethe standby gas standby gas treatment treatment vent vent at 442001N34117 (pa. at 442001N34117 (pa. Grid Grid System. System. The The location location codes are based codes are based onon both both distance distance and and direction direction from from thethe SSES. SSES. The The letters letters inin the the location codes location codes indicate indicate if if the the monitoring monitoring 1ocations 1ocations areare on on site site (within (within the the site site boundary) or, boundary) or, if if they are not they are not onon site, site, the the approximate approximate distances distances of of the the locatioris locatioris from the from the SSES SSES as as described described below: below: on site S -- on S site E- 4-5 E- 4-5 miles miles A- <1 A- <1 mile mile F -- 5-10 F 5-10 miles miles B 2 B 2 miles miles G -- 10-20 G 10-20 miles miles C -- 2-3 C 2-3 miles miles H- >20miles H- >20miles D 4 D 4 miles miles The numbers preceding The numbers preceding the the letters letters inin the the location location codes codes provide provide the the directions directions of of the monitoring the monitoring locations locations from from the the SSES SSES by by indicating indicating thethe sectors sectors in in which which they are they are located. A located. A total total of of 1616 sectors sectors (numbered (numbered 11 through through 16)16) equally equally divide divide an an imaginary circle imaginary circle onon aa map map ofof the the SSES SSES and and its its vicinity, vicinity, with with thethe SSES SSES at at the the center center of the of the circle. circle. The The middle middle of of sector sector 11 isis directed directed due due north north (N). Moving clockwise (N). Moving clockwise from sector from sector 1,1, the the sector sector immediately immediately adjacent adjacent to to sector sector 11 is is sector sector 2, 2, the the iniddle iniddle of of which is which is directed directed duedue north, north, northeast northeast (NNE). Continuing to (NNE). Continuing to move move clockwise, clockwise, the the sector numbers sector numbers increase increase to to 16, 16, which which is is the the north, north, northwest northwest sector. sector. The numbers following The numbers following the the letters letters inin the the location location codes codes areare used used toto differentiate differentiate sampling locations sampling locations found found inin the the same same sectors sectors at at approximately approximately the the same same distances distances from the from the SSES. SSES. b) b) No actual1ocation is No actual1ocation is indicated indicated since since fish fish sampled sampled from from thethe Susquehanna Susquehanna River River at at or below or below the the SSES SSES discharge discharge diffuser:fish diffuser:fish are are also also sampJed sampJed from from LTAW. LTAW. c) c) No permanent locations No permanent locations exist; exist; sampJes sampJes are are taken taken based based on on avaiJabiJity. avaiJabiJity. Consequently, it Consequently, it is is not not necessary necessary to to assign assign aa number number following following the the 1etter 1etter in in the the location code. location code. 2004 Radiological 2004 Radiological Environmental Environmental Monitoring Monitoring ReportReport C-}o C-}o
APPENDIXD APPENDIXD 2004 Radiological 2004 Radiological Environmental Environmental Monitoring Monitoring Report Report
AppendixD 2004 LAND 2004 LAND USE USE CENSUS CENSUS RESULTS RESULTS The SSES Technical The SSES Technical Requirements Requirements requi'rerequi're that that aa census census be' be' conducted conducted annually annually during, during, the growing the growing seasonseason to to determine determine the'IOcation the'IOcation of of the the nearest nearest milk milk animal, animal, residence residence 'and
'and garden greater garden greater than than 50 50 m 2 2
m :: (approx. (approx. 500 ,ft2) producing 500 ,ft2) producing broad broad ))eaf.vegetati eaf.vegetati on' on' within within aa distance of distance of 8 km (approx. 8 km (approx. 5 5 miles) miles) in in each each of of the the 16 16 meteorological meteorological sectorssectors surrounding surrounding the SSES. the SSES. To To comply comply with with this this requirement, requirement, aa land-use land-use census census waswas conducted conducted for for thethe SSES during SSES during 2004.2004.
SUMMARY
SUMMARY
OF OF CHANGES CHANGES FROM FROM 2003 2003 TO TO 2004 2004 Residence Residence Census: Census: The residence The residence 'census
'census was was conducted conducted from from 11 11 'August
'August through through 15 15 September September 2004 2004 ..
.. Distances Distances of of the the nearest nearest residences residences from from theSusquehanna'SES theSusquehanna'SES in in the the 16 16 different, different, sectors ranged sectors ranged from from 0.5 0.5 (J .Futoma, sector (J .Futoma, sector 7) 7) to to 2.1 2.1 miles miles (R. (R. Barberi, Barberi, sector sector 4),4), with with an an average of average of approximately approximately 1.0 1.0 miles. miles. :.:. Changes Changes fromfrom the the 2003 2003 census census areare as as follows: follows: ';'; .,., .. -- :.:. 1)
- 1) F. Michael F. Michael (Sector (Sector 12).@
12).@ 1.~ mile mile rep]a~ed W. W. Kisner Kisner (deceased) (deceased) @ @ 1.1 1.1 mne. mne. 2)
- 2) H. Long H. Long (Sector (Sector 15)15) @ @ 0.8,mile 0.8,mile replaced.L.
replaced.L. HidIay HidIay (residence (residence unoccupied) unoccupied) @ @ .. 0.8 mile. 0.8 mile. ,, Garden Census: Garden Census: The garden census The garden census was was conducted conducted from from 11 11 August August through through 15 15 September September 2004.2004. Distances of Distances of thethe nearest nearest gardens gardens from from thethe Susquehanna Susquehanna SES SES inin the the 16 16 different different sectors sectors ranged from ranged from 0.6 0.6 miles miles (T. Scholl, sector (T. Scholl, sector 7) 7) toto 4.04.0 miles miles (P. (P. Culver, Culver, sector sector 16), 16), with with anan average of average 1.9 miles. of 1.9 miles. Changes Changes fromfrom the the 2003 2003 census census in in gardens gardens had had no, no, impact impact on on the: the: intended sampling intended sampling of of fruits fruits and and vegetables vegetables during during 2004. 2004. Because Because of of the the milk monitoring milk monitoring that is that is perfonned, perfonned, there there is is no no requirement requirement to to sample sample from from gardens gardens that that have have aa potential potential for the for the deposition deposition of
\\
of activity activity by' by',, way way of of the the airborne airborne pathway. pathway. Changes Changes fromfrom the the 2003 census are 2003 census are 'as
'as follows:
follows: 1)
- 1) M. Zaletko M. Zaletko (Sector(Sector 8)8) @@ 1.61.6 mi1~ replacedD.
replacedD. Dawson Dawson (no (no garden garden this this year) year) @ @ 1.5 mile. 1.5 mile. 2)
- 2) F. Michael F. Michael (Sector (Sector 12)
- 12) @ @ 1.31.3 mile mile replaced replaced W. W. Kisner Kisner (deceased)
(deceased) @1.1@1.1 mile. mile. 3)
- 3) P. Moskaluk P. Moskaluk (Sector (Sector 14)
- 14) @ 1.3 ~i1e had
@ 1.3 had aa garden garden in in 2004;'but 2004;'but notnot in in 2603.
2603. Dairy Animal Census: Dairy Animal Census: .,1 ;; ,,.. ,
.,1 ,. .,,; ;
Ten dairy Ten dairy animal animal sites sites were were identified identified in in the the census census conducted conducted from from 1212 through through 18 18 August 2004. August 2004. The The number number of of sites sites were were the the same same as as in in 2003. 2003. 90ws 90ws were were present present at at all all sites; no sites; no dairy dairy goats goats werewere found. found. ,:.-,i"
,:.-,i" ii *.
*. r,i ..
r,i 2004 Radiological 2004 Radiological Environmental Environmental Monitoring Monitoring ReportReport D-2 D-2
J' J' AppendixD Irrigation Irrigation .. Inigated fruits Inigated fruits and and vegetables vegetables were were monitored monitored at at one one indicator indicator location location during during 2004. 2004. No No other fields other fields within within 10 10 miles miles down down river river of of Susquehanna Susquehanna SES SES were were irrigated irrigated in in 2004, 2004, including the including the Lupini Lupini Farm. Farm. "Route "Route 9393 Nescopeck Nescopeck Field"Field" (11D2), (11D2), Chapin Chapin Farm Farm "Drake "Drake Field" (lIF2), Field" (lIF2), and and Zehner Zehner Farm Farm (llD!) (llD!) because because wet wet weather weather prevailed prevailed much much ofof the the spring and spring summer....The and summer The Lupini Lupini Farm Farm (12F7) (12F7) in in Mifflinville Mifflinville briefly briefly irrigated irrigated potatoes potatoes in in June 2004 June 2004 using using the the Susquehanna Susquehanna River River water. water. TABLE 11 TABLE Nearest residence, garden, Nearest residence, garden, and and dairy dairy animal animal in in each each ofof the the 16 16 meteorological meteorological sectors sectors within aa 5-mile within 5-mile radius radius of of the the Susquehanna Susquehanna Steam Steam Electric Electric Station, Station, 2004 2004 ..
*NEAREST NEAREST NEAREST NEAREST NEAREST SECTOR SECTOR DIRECTION DIRECTION RESIDENCE RESIDENCE GARDEN GARDEN DAIRY ANIMAL DAIRY ANIMAL 1
1 N N 1.3 mi 1.3 mi 3.2mi 3.2mi >5.0 mi
>5.0 mi 2
2 NNE NNE 1.0mi 1.0mi 2.3 mi 2.3 mi ii >5.0 mi
>5.0 mi 3
3 NE NE 0.9 mi 0.9 mi 2.7 mi 2.7 mi >5.0 mi
>5.0 mi 4
4 ENE ENE 2.1 mi 2.1 mi 2.4 mi 2.4 mi a,c,d,r,t' a,c,d,r,t' >5.0 mi
>5.0 mi 5
5 E E 1.4 mi 1.4 mi 1.8 mi 1.8 mi a,c, a,c, 4.5 mi 4.5 mi gg 6 6 ESE ESE 0.5 mi 0.5 mi 2.5 mi 2.5 mi 2.7 mi 2.7 mi 0 0 7 7 SE SE 0.5 mi 0.5 mi 0.6mi 0.6mi >5.0 mi
>5.0 mi 8
8 SSE SSE 0.6mi 0.6mi 1.6mi 1.6mi >5.0 mi
>5.0 mi 9
9 S S 1.0mi 1.0mi 1.1 mi 1.1 mi >5.0mi
>5.0mi 10 10 SSW SSW 0.9 mi 0.9 mi 1.2mi 1.2mi mi a,b,c,d,e,g 3.0 mi 3.0 a,b,c,d,e,g 11 11 SW SW 1.5 mi 1.5 mi 1.9 mi 1.9 mi >5.0mi
>5.0mi 12 12 WSW WSW 1.3 mi 1.3 mi 1.3 mi 1.3 mi 1.7 mi g,i 1.7 mi g,i 13 13 W W 1.2 mi 1.2 mi 1.2 mi 1.2 mi 5.0mi 5.0mi 14 14 WNW WNW 0.8 mi 0.8 mi 1.3 mi 1.3 mi >5.0mi
>5.0mi 15 15 NW NW 0.8mi 0.8mi 1.8 mi 1.8 mi mi
>5.0 mi
>5.0 16 16 NNW NNW 0.6mi 0.6mi 4.0mi 4.0mi 4.2 mi 4.2 mi aa Chickens raised for Chickens raised for consumption consumption at at this this location.
location. Ducks raised b Ducks b raised for for consumption consumption at at this this location. location. Eggs consumed C Eggs C consumed from from chickens chickens atat this this location. location. Geese raised d Geese d raised for for consumption consumption at at this this location. location. Pigs raised ee Pigs raised for for consumption consumption at at this this location. location. rr Turkeys Turkeys raised raised for for consumption consumption at at this this location. location. Fruits/vegetables raised g Fruits/vegetables g raised for for consumption consumption at at this this location. location. Rabbits raised h Rabbits h raised for for consumption consumption at at this location.
- this location.
- Beef cattle ii Beef cattle raised for consumption raised for consumption at at this this location.
location. D*3 2004 Radiological 2004 Radiological Environmental Environmental Monitoring Monitoring Report Report
Appendix D Appendix D jj Goats raised for Goats raised for consumption consumption atat this this location.* location.* kk Pheasants raised Pheasants raised for for consumption consumption at at this this location. location.
- II Sheep raised Sheep raised for for consumption consumption at at this this location.
location.
*No locations *No locations were were identified identified as as raising raising rabbits, rabbits, goats, goats, and and pheasants pheasants during during 2004 2004 ..
2004 Radiological 2004 Radiological Em'ironmcntal Em'ironmcntal Monitoring Monitoring Report Report D-4 D-4
APPENDIXE APPENDIXE 2004 Radiological 2004 Radiological Environmental Environmental Monitoring Monitoring Report Report E-l E-l
APPENDIXF APPENDIXF F-l F-l 2004 Radiological 2004 Radiological Environmental Environmental Monitoring Monitoring Report Report
APPENDIXG APPENDIXG 2004 Radiological 2004 Radiological Enl'ironmental Enl'ironmental Monitoring Monitoring Report Report G*l
AppendixG AppendixG The averages for The averages for indicator indicator a~d control control locations locations reported reported in in the the Summary Summary of of Data Data Table, Table, which summarizes which summarizes the the entire entire year's year's results results forfor the the SSES SSES REMP, REMP, were were calculated calculated using using all measured ..all measured values,values, when when available, available, whether whether or or not not they they were were reported reported in in Appendix Appendix II tables. Values tables. Values belowbelow thethe MDCs, MDCs, even even zeroes zeroes and and negatives, negatives, were were part part of of the the averaging averaging proces's for proces's for these these analysis analysis results. results. WhenWhen no no measured measured resultsresults areare available available in in these these cases, "LLD" cases, "LLD" is is reported. reported. Preferably, Preferably, the the averages reported in,~he,SummaryofData table averages reported table forfor sample sample media media thatthat are normally are normally col1ected col1ected continuously continuously are are determined determined using using onlyonly results results frorrifrorri continuously continuously collected samples. collected samples. Occasionally, Occasionally, grab samples are grab samples are taken taken for for these these media media when when equipment malfurictions equipment malfurictions or or other an0r!talies preclude other an0r!talies preclude or or otherwise otherwise perturbperturb routine routine .'.' continuous sampling. continuous sampling. TheseThese grabgrab samples samples are are taken taken to to minimize minimize the the time time periods periods whenwhen no sampling no sampling is is being being performed, performed, or, or, in in some some iflstances, iflstances, when when continuous continuous sampling sampling is is considered to considered to be be nonrepresentative. nonrepresentative. Because Because grab grab samples. samples. areare snapshots snapshots of of the the media media overover brief brief periods, periods, it it is is preferable preferable not not to average'the to average'the analysis analysis results results of of these these .~ampJes with with those those forfor continuously continuously collected collected composite samples. composite samples. However. However. when when equipmen~ malfunctions malfunctions are are protracted, protracted, relatively' relatively' Jarge periods Jarge periods of of time time could could be be entirely entirely unrepresented unrepresented by by averages averages if if the the results results from from grab grab analyses are sample analyses sample are not not considered. considered. Allowing analysis results Allowing analysis results for for grab grab samples samples to to be be weighted weighted equallyequally with with thosethose representing relatively representing relatively large large periods periods of time would of time would tend tend to to bias bias the the resulting resulting averages averages ,, unjustifiably towards unjustifiably towards the the conditions conditions at the times at the times that that thethe grabs grabs areare obtained. obtained. AveragesAverages obtained in obtained in this this way way might might lessless accurately accurately reflect reflect the the conditions conditions for for thethe combined combined period period of continuous of continuous samplingsampling and and grab grab sampling sampling than than ifif only only thethe results results fromfrom continuous continuous sampling were sampling were used. used. OnOn the the other other hand, hand, using using weighting weighting factorsfactors for for the the analysis analysis results results of grab of samples derived grab samples derived from from thethe actual time it actual time it ~akes to to collect collect those those samples samples would would lead to lead to the the grab grab sample sample analysis analysis results results having having aa negligible negligible effecteffect on on thethe overall overall average average and not and not justifying justifying the the effort effort involved. involved. Grab samples Grab samples collected collected in in lieu lieu ofof normitJ normitJ continuous continuous sampling sampling are are typically typically obtained obtained at at regular intervals corresponding regular intervals corresponding to to the the intervals intervals (weekly) (weekly) at at which which the the continuously continuously samples would collected samples collected would usually usually be be retrieved retrieved forfor eventual eventual compositing. compositing. For For example, example, grab samples grab samples are are collected collected once once aa week week but but may may be be composited composited monthly monthly in in place place of of continuously collected continuously collected samples samples that that would would normally normally be be retrieved retrieved weeklyweekly and and composited monthly. composited monthly. Since Since eacheach grab grab sample sample is is used used to to represent represent an an entire entire week, week, albeit albeit imperfect, it imperfect, it is is reasonable reasonable to to weight weight thethe analysis analysis results results the the same. same. Thus,Thus, the the results results ofof one weekly one weekly grab grab areare given given approximately approximately one-fourth one-fourth the the weight weight of of the the results results forfor aa monthly composite monthly composite sample sample collected collected continuously continuously for each of for each of the the four four weeks weeks in in aa month. Similarly, month. Similarly, the the analysis analysis results results ofof aa composite composite of of four four weekly weekly grab grab samples samples would would carry the carry the same same weight weight as as the the analysis analysis results results for for aa composite composite of of four four weeksweeks of of continuously collected continuously collected sample. sample. 2004 Radiological 2004 Radiological ED\'ironmental ED\'ironmental Monitoring Monitoring ReportReport
Appendix G Appendix G The last three The last three (3) (3) pages pages ofof Appendix Appendix G G are are corrections corrections to to the the 2000, 2000, 2002 2002 and and 2003 2003 Annual Radiological Annual Radiological Environmental Environmental Operating Operating Reports Reports Appendix Appendix G. G. The corrections to The corrections to the the 2002 2002 and and 2003 2003 Appendix Appendix G G are: are: 1)
- 1) under under the the LOCATION LOCATION WITH WITH THE HIGHEST THE HIGHEST MEAN MEAN column column for for air air particulates particulates -- Gross Gross Beta, Beta, the the range range ofof data data has has been revised.
been revised. TheThe previously previously reported reported r~nge was was calculated calculated incorrectly incorrectly due due toto aa spreadsheet error; spreadsheet error; 2)2) the the air air iodine iodine results results previously previously reported reported were were not not in in the the correct correct units (E-03 pCi/m3)~ thus units (E-03 thus the the values values were were reported reported 1,0001,000 times times lower lower than than the the correct correct values. Air values. Air iodine iodine results results from from the the analysis analysis laboratory laboratory areare reported reported inin pCi/ml. pCi/ml. The The analysis laboratory analysis laboratory results results for for air air iodine iodine were were notnot multiplied multiplied by by 1,000 1,000 toto correspond correspond withwith the units the units reported reported in in the the Appendix Appendix G G table. table. The corrections to The corrections to the the 2000 2000 Appendix Appendix G G are: are: 1) 1) under under the the ALL ALL INDICATOR INDICATOR LOCATIONS MEAN LOCATIONS MEAN columncolumn forfor air air particulates particulates -- Gross Gross Beta, Beta, the the mean mean value value and and corresponding range corresponding range have have been been revised; revised; 2) 2) under under thethe LOCATION LOCATION WITH WITH THETHE HIGHEST :MEAN HIGHEST :MEAN column. column. forfor air air particulates particulates -- Gross Gross Beta~ the the location, location, mean mean and and corresponding range corresponding range have have been been revised; revised; 3) the air
- 3) the air iodine iodine results results previously previously reported reported were not were not in in the the correct correct units units (E-03 (E-03 pCi/m pCi/m33), thus the
), thus the values values were were reported reported 1,000 1,000 times times lower than lower than the the correct correct values.
values. Air Air iodine iodine results results from from the the analysis analysis laboratory are.. laboratory are.. reported in reported pCilm33** The in pCilm The analysis analysis laboratory laboratory results results for for air air iodine iodine were were not not multiplied multiplied byby 1,000 to 1,000 to correspond correspond with with the the units units reported reported in in the the Appendix Appendix G G table. table. All All air air iodine iodine sample results sample results for for 2000, 2000, 2002, 2002, and and 2003 2003 were were less less than than LLD. LLD. After After correction correction thethe results are results are consistent consistent withwith previous previous SSES SSES operational operational history. history. The corrections outlined The corrections outlined above above do do not not impact impact anyany conclusions conclusions documented documented in in the the referenced reports. referenced reports. 2004 Radiological 2004 Radiological Environmental Environmental Monitoring Monitoring Report Report G*3
(' co. ('
~~. ,,
TABLEG TABLEG
SUMMARY
SUMMARY
OF OF DATA DATA FORFOR SSES SSES OPERATIONAL RADIOLOGICAL OPERATIONAL RADIOLOGICAL ENVIRONMENTAL ENVIRONMENTAL MONITORING MONITORING PROGRA..\f PROGRA..\f ** 2004 2004 NAMROFFACILITY: SUSQUEIJANNASTEAMELECTRICSTATION NAMROFFACILITY: SUSQUEIJANNASTEAMELECTRICSTATION LOCATION OF LOCATION OF FACILITY: FACILITY: LUZERNE LUZERNE COUNTY,COUNTY, PENNSYLVANIA PENNSYLVANIA Reporting Pertoe!: Reporting Pertoe!: Detember 29, Detember 29, 2003 2003 to to January Ui,200S January Ui,200S lort3 Page lort3 Page ANALYSIS AND ANALYSIS AND WWERllMIT WWERllMIT r..'UMDEROP r..'UMDEROP MEDIUMORPAnrwAY MEDIUMORPAnrwAY TOTALNtThIDnR TOTALNtThIDnR OF OF AlL INDICATOR AlL INDICATOR LOCAnONS LOCAnONS LOCAnoNwrmmGlIBST~mAN CONrROL LOCAnoN CONrROL LOCAnoN NONROUI1NB NONROUI1NB SAMI'IJID .. SAMI'IJID OF ANAL OF ANALYSE.~ mrrncnoN mrrncnoN l>mAN(3) l>mAN(3) NMm NMm t.mAN(3) t.mAN(3) l>mAN(3) l>mAN(3) REPORTED REPORTED (UNrrOFMEASUREMENn (UNrrOFMEASUREMENn rnRFORMED~l! ~ll.Dl (2) (2) RANGE RANGE DlSTANCR DlSTANCR AND AND DlREcnON DlREcnON RANGE RANGE RANGE RANGE ~mASUREMENrS!4} Ambient Ra1118t1on Ambient Ra1118t1on TLO TLO 253 253 2,OSB+OI (2301230) 2,OSB+OI (2301230) 9S2 9S2 4.56B+OI 4.56B+OI (4/4) (4/4) 1.98B+01 1.98B+01 (23 123) (23 123) 00 qtr.) (mRlstd. qtr.) (mRlstd. (1.46B+Ol (1.46B+Ol S.10B+Ol) S.10B+Ol) 0.2 0.2 rni rni 88 (4.28E+01 ** (4.28E+01 5.10B+0l) 5.10B+0l) (1.60E+Ol (1.60E+Ol 2.36B+01) 2.36B+01) Surfate Water Surfate Water GrossBrta GrossBrta 49 49 4 4 5.73B+OO 5.73B+OO (36 136) (36 136) 2S7 2S7 1.10E+Ot 1.10E+Ot (12/12) (12/12) 2.84B+OO 2.84B+OO (13 II 13) (13 13) 00 (pOn) (pOn) (1.14E+OO (1.14E+OO 1.59E+OI) 1.59E+OI) 0.1 0.1 rni rni NNE NNE (6.5SE+OO (6.5SE+OO t.59E+01) t.59E+01) (6. lOE-O II (6. lOE-O 7.35E+OO) 7.35E+OO) Tritium Tritium 49 49 2000 2000 l.SSE+03 l.SSE+03 (36/36) (36/36) 2S7 2S7 4.4SB+03 4.4SB+03 (12 1(2) (12 1(2) 7.S7B+OI 7.S7B+OI (13 113) (13 113) 00 (.7.1SB+Ol (.7.1SB+Ol 1.84E+04) 1.84E+04) 0.1 0.1 rni rni NNE NNE (2.60E+02 (2.60E+02 1.84E+04) 1.84E+04) (.1.57E+0I (.1.57E+0I 2.44E+(2) 2.44E+(2) Iodine-131 Iodine-131 36 36 4.93E-OI 4.93E-OI (22/24) (22/24) 2S7 2S7 7.46E-OI 7.46E-OI (11/12) (11/12) 3.S9E-OI 3.S9E-OI (11 112) (11 112) 00 (.3.00E-OI (.3.00E-OI 1.39E+OO) 1.39E+OO) 0.1 0.1 rni rni NNE NNE (I.OOE-02 (I.OOE-02 1.39E+OO) 1.39E+OO) (.1.00E-02 (.1.00E-02 7.40E-Ol) 7.40E-Ol) GammaSpee GammaSpee
,K-40
,K-40 49 49 .. ~3.89E-Ol (36/36)
(36/36) .. 686 686 6.23B+OO 6.23B+OO (13 113) (13 113) 6.23E+OO 6.23E+OO (13 It3) (13 It3) 00 (*3.600+01 2.10E+Ol) 2.10E+Ol) O.! O.! rni rni ESE ESE (.t.l0E+OI (.t.l0E+OI 2.90E+01) 2.90E+01) (.l.lOE+OI (.l.lOE+OI 2.90B+0l) 2.90B+0l) Mn-S4
.. Mn-S4 49 49 IS IS .3.70E-OI
.3.70E-OI (36/36)
(36/36) 6S5 6S5 .1.05E-OI
.1.05E-OI (12/12)
(12/12) .1.I9E*Ot (I3it3) (I3it3) 00 (-3. II OE+OO (-3. OE+OO 1.40E+OO) 1.40E+OO) 0.9 0.9 rni rni ESE ESE (.1.20E+OO (.1.20E+OO 9.00E-01) 9.00E-01) (*l.OOE+OO 1.50E+OO) 1.50E+OO) Co-58 Co-58 49 49 15 15 -4.52E-Ol
-4.52E-Ol (36 /36)
(36 /36) 656 656 .2.66E-Ol (13 113)
.2.66E-Ol .. (13 113) *2.66E-01 (13 II 13)
(13 13) 0 0 (.2.40E+OO (.2.40E+OO t.20E+OO) t.20E+OO) O.S O.S rni rni ESE ESE (-1.30E+OO (-1.30E+OO 7.00E-Ol) 7.00E-Ol) (-1.30E+OO (-1.30E+OO 7.00E-Ol) 7.00E-Ol) Fe-59 Fe-59 49 49 30 30 3.07E-OI 3.07E-OI (36/36) (36/36) 6SS 6SS 1.63E+OO 1.63E+OO (12/12) (12/12) 2.4SE-02 2.4SE-02 (13 /13) (13 /13) 00 (-1.18E+OI (-1.18E+OI 7.30E+OO) 7.30E+OO) 0.9 0.9 rni rni ESE ESE (-2.30E+OO (-2.30E+OO 3.90E+OO) 3.90E+OO) (-4.70E+OO (-4.70E+OO 4.90E+OO) 4.90E+OO) co-em co-em 49 49 15 15 4.98E-02 4.98E-02 (36/36) (36/36) LTAW LTAW 2.75E-Ol 2.75E-Ol (12/12) (12/12) *3.18E-Ol (13 // (3) (13 (3) 00 (.1.70E+OO (.1.70E+OO 1.70E+OO) 1.70E+OO) onsite .. onsite NE*ESE (.1.7~E+OO .. 1.70E+OO) .. (-1.40E+OO 1.70E+OO) (-1.40E+OO S.OOE-OI) S.OOE-OI)
.. Zn-65 Zn-65 49 49 30 30 1.93E-02 1.93E-02 (36' 36)
(36' 36) LTAW LTAW 8.75E-Ol 8.75E-Ol (12/12) (12/12) -1.24E+OO
-1.24E+OO (13 "" (3)
(13 (3) 00 (4.40E+OO (4.40E+OO !.OOE+OO)
!.OOE+OO) on site on site NE.ESl? (.3.20E+OO NE.ESl? (.3.20E+OO -- 8.00E+OO) 8.00E+OO) (-4.20E+OO
(-4.20E+OO 1.70E+OO) 1.70E+OO)
TABLEG TABLEG
SUMMARY
SUMMARY
OF OF DATA DATA FORSSES FORSSES OPERATIONAL RADIOLOGICAL OPERATIONAL RADIOLOGICAL ENVIRONMENTAL ENVIRONMENTAL MONITORING MONITORING PROGRAM-PROGRAM- 2004 2004 NAMEOFFACILlTY: SUSQUEllANNASTEAMELECTRICSTATlON NAMEOFFACILlTY: SUSQUEllANNASTEAMELECTRICSTATlON LOCATION OF LOCATION OF FACILITY: FACILITY: LUZERNE LUZERNE COUNTY, COUNTY, PENNSYLVANIA PENNSYLVANIA Reporting Period: Reporting Period: December 29, December 29, 2003 2003 to to January 26, January 26, 2005 2005 PageloflJ PageloflJ ANALYSIS AND ANALYSIS AND LOWERlJMIT LOWERlJMIT NmWEROF NmWEROF MEDIUM ORPATIlWAY TOTALNmWER MEDIUM ORPATIlWAY TOTALNmWER OF OF AIL INDICATOR AIL INDICATOR LOCAnONS LOCAnONS LOCAnoNwmtlRGHEST LOCAnoNwmtlRGHEST MIlAN MIlAN CONTROLLOCAnON CONTROLLOCAnON NONROtmNB NONROtmNB SAMPLED SAMPLED OF ANALYSES OF ANALYSES DlITECllON DlITECllON MEAN (3) MEAN (3) NA.\fll NA.\fll MEAN (3) MEAN (3) MEAN(l) MEAN(l) REPORTED REPORTED (UNIT OF (UNIT OF MEMUREMENl) MEMUREMENl) PERl:ORMED PERl:ORMED {I! {I! (UD!(2! (UD!(2! RANGE RANGE DISTANCE AND DISTANCE AND D1REGnON D1REGnON RANGE RANGE RANGE RANGE MEMUREMENfS!4! MEMUREMENfS!4! Surfate Water (conl) Surfate Water (conl) Zr*95 49 49 30 30 -6.98B-Ol (36/36)
-6.98B-Ol (36/36) 257 257 2.41E-Ol (121 2.41E-Ol (121 12)12) (13 113) 1.28E-Ol (13 1.28E-Ol 113) 0 0
(pClI1) (pClI1) (*5.70£+00 2.50E+00) 2.50E+00) (l.OOE-OI (l.OOE-OI mi mi NNE NNE (.1.70£+00 (.1.70£+00 -- 2.50E+00) 2.50E+00) (.3.ooE+00 (.3.ooE+00
- 4.50E+00) 4.50E+00) t-'b-95 t-'b-95 49 49 15 15 -4.67£-01 (36/36)
-4.67£-01 (36/36) 257 257 2.90E-Ol (12/12) 2.90E-Ol (12/12) -5.94£-01 (13 113)
-5.94£-01 (13 113) 00
(*3.10£+00 4.40E+00) 4.40E+00) (1.ooE-Ol (1.ooE-Ol mi mi NNE NNE (.1.70E+00 (.1.70E+00 4.40E+00) 4.40E+00) (-2.40E+00 (-2.40E+00 2.50E+00) 2.50E+00) Cs-134 Cs-134 49 49 15 15 (36/36) 2.91B-Ol (36/36) 2.91B-Ol 6S5 6S5 4.11E-Ol (12/12) 4.11E-Ol (12/12) (13 II 13)
*3.76E.oJ (13 13) 0 0
(*2.ooE+00 2.30E+00) 2.30E+00) (9.ooE-Ol (9.ooE-Ol "U "U ESE ESE (*2.ooE+oo
- 2.30E+00) 2.30E+00) (.2. 70E+00
(.2.70E+00
- 2.60E+00) 2.60E+00)
Cs-137 Cs-137 49 49 18 18 -7.78E..02 (36/36)
-7.78E..02 (36/36) 2S7 2S7 1.75E-Ol (12 II 12) 1.75E-Ol (12 12) (13 II 13)
*3.88E-OI (13 13) 00
(*2.50£+00
- 2.30E+00) 2.30E+00) (1.ooE-OI (1.ooE-OI mi mi NNE NNE (*8.ool!-Ol 1.90E+00) 1.90E+00) (*1.90E+00
- 6.ooE-Ol) 6.ooE-Ol)
Da*140 49 49 60 60 -6.04E..02 (36/36)
-6.04E..02 (36/36) LTAW LTAW 1.92£-01 (12/12) 1.92£-01 (12/12) (13 113)
*1.27£'01 (13 113) 0 0
(*5.50£+00
- 4.60E+00) 4.60E+00) onsile onsile NE-ESE NE-ESE (.3.10£+00
(.3.10£+00
- 4.60E+00) 4.60E+00) (-6.00£+00
(-6.00£+00
- 4.ooE+00) 4.ooE+00)
La*140 49 49 15 15 *7.56E..02 (36' 36) (36' 36) LTAW LTAW 2.08E.oI (12 II 12) 2.08E.oI (12 12) *1.5lE-01 (13 113) (13 113) 0 0 (-6.30E+OO (-6.30E+OO
- S.30E+00)
S.30E+00) on site on site NE-BSE NE-BSE (.3.60£+00 (.3.60£+00
- 5.30E+00) 5.30E+00) (-6.90£+00
(-6.90£+00
- 4.50IJ,+00) 4.50IJ,+00)
(( cc.. ((
(. (' ( TADLEG TADLEG
SUMMARY
SUMMARY
OF OF DATA DATA FOR FOR SSES SSES OPERATIONAL RADIOLOGICAL OPERATIONAL RADIOLOGICAL ENVIROmmNT ENVIROmmNTAL AL MOl\lTORING MOl\lTORING PROGRAM PROGRAM -- 20042004 NAME OF NAME OF FACILITY: FACILITY: SUSQUEHANNA SUSQUEHANNA STEAM STEAM ELECTRIC ELECTRIC STATION STATION LOCATION OF LOCATION OF FACILITY: FACILITY: LUZERNE LUZERNE COUNTY. COUNTY. PENNSYLVANIA PENNSYLVANIA Rtportlng Ptriod: Rtportlng Ptriod: 29, 2003 DrC'tmbrr 29, DrC'tmbrr 2003 to to January 2tl, January 2tl, 2005 2005 Page3ort3 Page3ort3 ANALYSIS AND ANALYSIS AND LOWERUMIT LOWERUMIT NUMBER OF NUMBER OF MEDIUM MEDIUM OROR PATHWAY PATHWAY TOfALNmffiER TOfALNmffiER OF OF AIL INDICATOR AIL INDICATOR LOCATIONS LOCATIONS LOCATION wrm mGIlEST LOCATION wrm mGIlEST MEAN MEAN CONTROL LOCATION CONTROL LOCATION NONROUI'll'."B NONROUI'll'."B SAMPLED SAMPLED OFANALYSBS OFANALYSBS DETI!CIlON DETI!CIlON MEAN (3) MEAN (3) NAMB NAMB l-IDAN(3) l-IDAN(3) l-mAN(3) l-mAN(3) REPORTED REPORTED OF l-IDASUREMENr) (UNIT OF (UNIT l-IDASUREMENr) PERFORMED PERFORMED ~ll (UD~(2) RANGE RANGE DISTANCE AND DISTANCE AND DIRECTION DIRECTION RANGE RANGE RANGE RANGE l-IDASUREMENTS(4) l-IDASUREMENTS(4) Potable Water Gross Alpha 12 I.4SE*01 (12/12) 12112 1.45E-OI (12 112) Only indicator 0 (pCiA) (4.92E-OI
- 8.44B*OI) 26 mi WSW (4.92E*Ol
- B.44E*OI) .stations sampled for this medium.
Gross Beta 12 4 1.9IE+00 (12/12) 12H2 1.9IE+00 (12 I 12) 0 (7.3SE-Ol - 3.(l9R+00) 26 mi WSW (7.3SR-Ol 3.09B+00) Iodi.ne-I31 12 1 1.40E-Ol (12/12) 12H2 1.40E-01 (12/12) 0 (.1.70B-OI
- 4.90E*OI) 26 mi WSW (-1.70E*Ol
- 4.90E*Ol)
Tritium 12 2000 7.41E+OI (12/t2) t2112 7.4lE+0l (t2 It2) 0 (*1.7SE+Ol
- 1.95E+02) 26 mi WSW (*1.75E+OI
- 1.95E+02)
Gamma Spec K40 12 *6.8SE-Ot (12112) 12112 *6.BSE*OJ (12/12) 0 (*1.S0E+Ol - 1.10E+Ol) 26 mi WSW (*1.50E+Ol - 1.10E+Ol) Mn-54 12 IS -1.SSE*OJ (12/12) 12112 *l.SSE-Ol (12/12) 0 (-1.30E+00 8.00E-0l) 26 mi WSW (*1.30E+OO
- B.OOE-OI)
Co-58 12 IS 4.40B-Ol (12 I 12) 12H2 4o40E-Ot (12 I 12) 0 (*1.S0E+OO 1.20B+OO) 26 mi WSW (.1.S0E+OO ' - 1.20E+00) Fc,.59 12 30 1.06B+00 (12/t2) 12112 1.06E+00 (12/12) 0 (4.IOE+OO - 3.80E+00) 26 mi WSW (4.10B+00 - 3.80E+OO) Co-50 12 15 1.94B-01 (12/12) 12H2 1.94B-Ol (12/12) 0 (*1.30E+OO 1.80E+00) 26 mi WSW (*t.30E+00
- 1.80E+OO)
Zn-6S 12 30 *6.8m-OJ (12/12) 12112 *6.Sm-OI (12/12) 0 (-S.lOE+oo
- B.50B+OO) 26 mi WSW (-B.IOE+oo
- S.50E+00)
Zr*95 12 30 -3.72B*Ol (12/t2) 12H2 -3.72E-Ot (12/12) 0 (4.20E+00
- 3.10E+00) 26 mi WSW (4.20B+OO
- 3. I OE+OO)
TAULEG TAULEG
SUMMARY
SUMMARY
OF OF DATA DATA FORSSES FORSSES OPERATIONAL RADIOLOGICAL OPERATIONAL RADIOLOGICAL ENVIRONMENTAL ENVIRONMENTAL MONITORING MONITORING PROGRAM* :W04 :W04 NAME OF NAME OF l<'ACILITY: l<'ACILITY: SUSQUEHANNA SUSQUEHANNA STEAM STEAM ELECTRIC ELECTRIC STATION STATION LOCATION OF LOCATION }t'ACILITY: LUZm{NE OF }t'ACILITY: LUZm{NE COUNTY. COUNTY. PEr--,...SYLVANIA PEr--,...SYLVANIA RellOrting Period: RellOrting Period: 29. :WO) December 29. December :WO) to to 26. :WOS January 26. January :WOS Page" of Page" of 13 13 ANALYSIS AND ANALYSIS AND LOWERllMlT LOWERllMlT t.'UMBEROF t.'UMBEROF MEDIUM OR PATIIWAY MEDIUM OR PATIIWAY Tar ALNUMBER TarALNUMBER OF OF AlLJNDICATORLOCATIONS AlLJNDICATORLOCATIONS LOCATION 'Wmr IIIGlIBST LOCATION 'Wmr MEAN IIIGlIBST MEAN CONIROLLOCATION CONIROLLOCATION NONROUllNB NONROUllNB SAMPLED SAMPLED OFANALYSBS OFANALYSBS DEl'ECTION DEl'ECTION MEAN (3) MEAN (3) N~m ..mAN
..mAN (3) (3) ..mAN
..mAN (3)
(3) REPORTED REPORTED !UNlTOFMBASUREMENT) PERFORMBDPl !UNlTOFMBASUREMENT) PERFORMBDPl (llD)(2) (llD)(2) RANGE RANGE DISTANCE AND DISTANCE AND DIRECTION DIRECTION RANGE RANGE RANGE RANGE MEA<;UREMENTS~4l Potable Water Potable Water (cont) (cont) Nb-95 Nb-95 12 12 15 15 -So4IE-OI (12/12)
-So4IE-OI (12/12) 12H2 12H2 -5.4lE-0i (12
-5.4lE-0i 112)
(12 112) Only indicator Only indicator 0 0 (pCiIl) (pCiIl) (-2.70E+00 (-2.70E+00 -- 6.00E-OI) 6.00E-OI) 26 26 mi WSW mi WSW (-2.70E+00 (-2.70E+00 -- 6.00E-OI) 6.00E-OI) stations sampled for stations sampled this medium. this medium. for Cs-l34 Cs-l34 12 12 15 15 2.92E-Ol (12/12) 2.92E-Ol (12/12) 12112 12112 2.92E-Ol (12/12) 2.92E-Ol (12/12) 0 0 (-1.ooE+oo (-1.ooE+oo 2.40E+00) 2.40E+00) 26 26 mi WSW mi WSW (-1.00E+00 (-1.00E+00 2.40E+00) 2.40E+00) Cs-137 Cs-137 12 12 18 18 -lo4lE-Ol (12
-lo4lE-Ol (12 JJ 12)
- 12) 12H2 12H2 -1.4lE-OI (12/12)
-1.4lE-OI (12/12) aa
(-1.80E+00 (-1.80E+00 1.ooE+00) 1.ooE+00) 26 26 mi WSW mi WSW (-1.80E+00 (-1.80E+00 -- l.ooE+OO) l.ooE+OO) Ua-140 Ua-140 12 12 60 60 2.28E+00 (12 2.28E+00 (12 II 12)
- 12) 12H2 12H2 2.28E+00 (12/12) 2.28E+00 (12/12) 0 0
(-3.IOE+00 (-3.IOE+00 7.50E+00) 7.50E+00) 26 26 mi WSW mi WSW (-3.10E+00 (-3.10E+00 7.50E+00) 7.50E+00) La*140 12 12 15 15 2.60E+OO (12 2.60E+OO (12 11 12)
- 12) 12H2 12H2 2.60E+oo (12/12) 2.60E+oo (12/12) 0 0
(-3.60E+00 (-3.60E+00 -- 8.60E+00) 8.60E+00) 26 26 mi WSW mi WSW (-3.60E+00 (-3.60E+00 -- 8.60E+00) 8.60E+00)
- c. c.
Q*7 ('
c* ( C. TABLEG TABLEG
SUMMARY
SUMMARY
OF OF DATA DATA FOR FOR SSES SSES OPERATIONAL RADIOLOGICAJ4 OPERATIONAL RADIOLOGICAJ4 ENVlROmmNT ENVlROmmNTAL AL MONITORING MONITORING PROGRAM* 2004 2004 NAl\m OF NAl\m OF FACILITY: FACILITY: SUSQUEHANNA SUSQUEHANNA STEAJ\.f STEAJ\.f ELECTRIC ELECTRIC STATION STATION LOCATION OF LOCATION OF FACILITY: FACILITY: LUZERNE LUZERNE COUNTY, COUNTY, PENNSYLVANIA PENNSYLVANIA Reponing Perioll: Reponing Perioll: Derember 19, Derember 2003 19, 2003 to to January 26, January 26, 1005 1005 PlI2t or 13 PlI2t 55 or 13 ANALYSIS AND ANALYSIS LOWERUMlT AND LOWERUMlT NUMBER OF NUMBER OF MEDIUMORPATIlWAY MEDIUMORPATIlWAY TOTALNUMIU!R TOTALNUMIU!R OF OF INDICATOR LOCATIONS AU. INDICATOR AU. LOCATIONS LOCATIONWnllInGIlESTloffiAN LOCATIONWnllInGIlESTloffiAN CONTROL LOCATION CONTROL LOCATION NONROUl1NB NONROUl1NB SAMPLED SAMPLED OFANALYSns OFANALYSns DETECOON DETECOON MEAN (3) MEAN (3) NA\ffi NA\ffi lomAN (3) lomAN (3) MEAN (3) MEAN (3) RnPORTI!D RnPORTI!D OF lomAC;URnMnNT) ~UNlT OF lomAC;URnMnNT) PERFORMED PERFORMED ~1! (UD~(2) RANGn RANGn DISTANCB AND DISTANCB AND DIRECOON DIRECOON RANGn RANGn RANGn RANGn MEASUREMENrS!4~ Fish OammaSpec (pCi/kg wet) K-40 t3 3.53E+03 (1/7) LTAW 3.68E+03 (tIl) 3ABE+03 (6/6) 0 (2.92E+03 - 4.12E+03) o.n site NE*ESE {3.68E+03
- 3.6BE+03) (2.74E+03
- 4.10E+03)
Mn-54 13 130 7. 19E*Ot (1/7) 2I1 1. 11E+Ol (6/6) 1.11E+Ot (6/6) 0 (.B.54E+00 - 6.79E+00) 30 rni NNE (-1.77B+00 - 3.25E+0I) (-1.77B+00 - 3.25E+Ol) Co-58 13 130 -6.02E+00 (1/7) INn -4.26E+00 (6/6) -1.52B+Ol (6/6) 0 (-2.12B+OI ~ 2.30E+OI) 0.9-1.4 rni ESE (*2.12B+Ol
- 2.30E+Ol) (-4.l4E+Ol -. 2.20E+01)
Fe-59 13 260 *2.68E+Ol (1/7) LTAW 2.64E+Ol (1 II) -S.83E+00 (6/6) 0 (-7.36E+Ot - 2.64E+01) on site NB-ESE (2.64E+Ol
- 2.64E+Ol) (-3.ooE+Ol - 9.66E+OO)
Co-GO 13 130 2.03E+oo (1/7) INn 3.S5E+00 (6/6) 3.OOE+OO (6/6) 0 (-7.06E+00
- 1.61E+01)' 0.9-1.4 mi ESE (*1.22E+OO
- 1.61E+Ol) (.9.mm~oO - 2.80E+OI),
Zn-65 13 260 6.40E+00 (1/7) LTAW 1.04E+Ol (I 11) -3.32E+Ol (6/6) 0 (-205E+Ol - 5.72E+0I) on site NE*ESE (1.04E+Ot l.04E+OI)' (-9.06E+Ol
- 1.12B+OI)
Zr*9S 13 1.60E+oo (1/7) LTAW 2.02E+Ot (I II) S.03E+00 (6/6) 0 (.2.42E+01 - 2.02E+01) on site NE-ESE (2.02B+01 - 2.02E+01) (-3.41E+Ol 5.33E+Ol) Nb-95 13 -4.29E+OO (1/7) 2H 1.37E+Ol (6/6) 1.37E+Ol (616) 0 (-3.0BE+01 1.68E+01) 30 mi NNE (-6.t6E+00
- 3.61E+Ol) (.6.16E+00
- 3.61E+0l)
Cs-l34 13 130 -2.69E-OJ (1/7) IND -2.50B-02 (616) -1.32E+Ol (6/6) 0 (-S.4tE+oo
- S.90E+oo) 0.9-1.4 rni ESE* (*S.41E+00
- S.90E+OO) (-2.48E+Ol
- 3.54E+OO)
Cs*137 13 150 4.60E+OO (1/7) IND 4'62E+OO (6/6) 4.S9E+OO (6 (6) 0 (.t.87E+Ol
- 2.27E+01) 0.9-1.4 .mi ESE, (.t.87E+Ol
- 2.27E+Ol) (-t.47E+0l - 2.59E+OI)
Ba*140 13 1.14E+02 (1/7) IND 1.46E+02 (6/6) 2.92E+01 (6/6) 0 (-8.05E+OI
- 2.86E+02) 0.9-1.4 rni ESE, (I.92E+Ol - 2.86E+02) (.gJ)6E+Ot - 9.78E+01)
La*t40 13 *S.29E+00 (1/7) IND -3.68E+OO (616)
- t.89E+0 1 (6/6) 0
(-3.60E+Ol 1.79E+01) 0.9*104 rni ESE. (.2.SBE+Ol - 1.79E+Ol) (-g.29E+Ol 3.35E+Ol) Q*s
TAllLEG TAllLEG
SUMMARY
SUMMARY
OF OF DATA DATA FOIl FOIl SSES SSES Ol)ERATIONAL RADIOLOGICAL Ol)ERATIONAL RADIOLOGICAL ENVIRONMENTAL ENVIRONMENTAL MONITORING MONITORING PROGRAM* 2004 2004 NAME OF NAME OF FACILITY: FACILITY: SUSQUEIIANNA SUSQUEIIANNA STEAM STEAM ELECTRIC ELECTRIC STATION STATION LOCATION 01<' LOCATION .'ACILITY: LUZERNE 01<' .'ACILITY: LUZERNE COUNTY, COUNTY, PENNSYLVANIA PENNSYLVANIA H.eportiug Period: H.eportiug Period: December 29, December 29, 2003 2003 to to January 26. January 26. 200S 200S Page 60f13 Page 60f13 ANALYSIS AND ANALYSIS AND LOWBRIDtrr LOWBRIDtrr NUMBER OF NUMBER OF MEDIUM ORPATIIWAY TOTALNmIDER MEDIUM ORPATIIWAY TOTALNmIDER OF OF AlL INDICATOR AlL INDICATOR LOCATIONS LOCATIONS LOCATIo.~wrrnmOlmsr MEAN MEAN CONTROL LOCATION CONTROL LOCATION NONROtmNB NONROtmNB SAMPLED SAMPLED OF ANALYSES OF ANALYSES DETECTION DETECTION MEAN (3) MEAN (3) NAME. NAME. MEAN (3) MEAN (3) MEAN (3) MEAN (3) REPORTED REPORTED (UNIT OF (UNIT OF MEA.smmMIl.NTI MEA.smmMIl.NTI PERFORMED !'! PERFORMED !'! (2)
~11J) (2) RANGE!
RANGE! DISTANCB DIST ANCB AND AND DIREcnON DIREcnON RANGE RANGE RANGE RANGE ~mASUREMENfS!4! Sediment OammaSpec (pCilkg dry) Be-7 8 I.07E+02 (6/6) 2B S.S6E+02 (2/2) S.S6E+02 (2/2) 0 (-1.04E+02 - S.70E+02) 1.6 mi NNE (l.33E+OO - 1.llE+03) (1.33E+OO - 1. llE+03) K-40 8 1.31E+04 (6/6) LTAW 1.S1E+04 (2/2) 1.48E+04 (2/2) 0 (9.39E+03 . 1.S4E+04) onsile NE*ESE (1.49E+04 - 1.S3E+04) (1.36E+04 - 1.60E+04) Mn-S4 8 6.54E+OO (6 J 6) 7B l.03E+Ol (2/2) S.68E+OO (2/2) 0 (-9.61E+OO - 1.19E+Ol) 1.2 mi SE (S.72E+OO
- 1.19E+Ol) (S.S4E-Ol 1.OSE+Ol)
Co-58 8 -1.17E+0l (6/6) 2B 2.7SE+OO (2/2) 2.78E+OO (2/2) 0 (-3.S7E+Ol 3.34E+OO) 1.6 mi NNE (S.72E+OO 5.8SE+OO) (-2.S2E-Ql S.8SE+OO) Fe-59 8 -2.24E+Ol (6/6) 2B 2.68E+Ol (2/2) 2.6&E+Ol (2/2) 0 (*1.20E+02 - 2.S1E+0l) 1.6 1m NNE (1.40E+Ol 3.9SE+Ol) (l.40E+Ol 3.9SE+01) Co-60 8 1.40E+OO (6/6) 12F I.08E+Ol (2/2) 8.S7E+OO (2/2) *0 (-1.46E+Ol 1.27E+01) 6.9 mi WSW (B.93E+OO 1.27E+Ol) (*9.87E+OO 2.76E+OI) Zn-6S S 9.S7E+OO (6/6) 7B 3.91E+OI (2/2) 1.49E+Ol (2/2) 0 (*S.29E+Ol . S.73E+Ol) 1.2 mi SE (2,09E+OI
- S.73E+OI) (9.48E+OO - 2.04E+Ol)
Zr-9S S 9. 13E+OO (6/6) LTAW 4.t7E+OI (2/2) 8.8SE*Ot (2/2) 0 (*2.61E+OI 8. 17E+OI) on site NE*ESE (l.67E+OO - S.l7E+Ol) (.2.39E+OO . 4. 16E+OO) Nb-9S 8 -3.19E+OO (6/6) .12F 1.29E+Ol (2/2) -l.l7E+Ol (2/2) 0 (*3.67E+Ol - 3.33E+0l) 6.9 mi WSW (*7.S2E+OO 3.33E+OI) (*2.75E+Ol 4.01E+OO) Cs*l34 8 150 *1.61E+OO (6/6) 2B B.27E+OO (2/2) S.27E+OO (2/2) 0 (*1.48E+Ol 1.7SE+OI) 1.6 mi NNE (S.93E+oo
- 1.06E+OI) (S.93E+OO l.06E+OI)
Cs-137 S 180 2.19E+Ol (6/6) 7B 7. 19E+Ol (2/2) 6.SSE+Ol (2/2) 0 (*2.02E+OI I.03E+02) 1.2 mi SE (4.08E+Ol
- 1.03E+02) (3.96E+OI 9.20E+Ol)
Ba*140 8 *9.07E+Ol (6/6) 78 4.60E+Ol (2/2) *1.46E+02 (2/2) 0 (*S.63E+02 8.36E+Ol) 1.2 mi SE (3.4lE+Ol - S.78E+OI) (.2.20E+02 - -7.23E+Ol) (HI ( c. (
c* ( '" C~* TADLEG TADLEG SUJ\IMARY SUJ\IMARY OFOF DATA DATA FORFOR SSES SSES OPERATIONAL RADIOLOGICAL OPERATIONAL ENVlROmmNTAL RADIOLOGICAL ENVlROmmNT AL MONITORING MONITORING PROGRAM. PROGRAM. 2004 2004 NAME OF NAME OF FACILITY: FACILITY: SUSQUEUANNA SUSQUEUANNA STEAM STEAM ELECTRIC ELECTRIC STATION STATION LOCATION OF LOCATION OF FACILITY: FACILITY: LUZERNE LUZERNE COUNTY, COUNTY, PENNSYLVANIA PENNSYLVANIA Reporting Perioel: Reporting Perioel: Duember 29, Duember 29, 2003 2003 to to January 26, January 26, 2005 2005 Page70rtJ Page70rtJ ANALYSIS AND ANALYSIS LOWERUMlT AND LOWERUMlT NUMDEROF NUMDEROF MEDIUM MEDIUM OR OR PATlIWAY PATlIWAY Tar NUMDER AI. NUMDER TarAI. OF OF AU. INDICATOR AU. INDICATOR LOCATIONS LOCATIONS LOCATION WInI LOCATION WInI InOHEST InOHEST MEAN MEAN CONTROL LOCATION CONTROL LOCATION NONRounrm NONRounrm SAMPLED' SAMPLED' OF ANALYSES OF ANALYSES DIrrECflON DIrrECflON MHAN(3) MHAN(3) NA1>ffi NA1>ffi MEAN (3) MEAN (3) l.ffiAN(3) l.ffiAN(3) REPORTED REPORTED (UNIT OFl.ffiASUREMENn (UNIT OFl.ffiASUREMENn PERFORMED PERFORMED (1)(1) (UD)(2) (UD)(2) RANGE RANGE DISTANCE AND DISTANCE AND DIRECflON DIRECflON RANGE RANGE RANGl! RANGl! l.ffiAStJRIThffiNTS(4~ l.ffiAStJRIThffiNTS( Sediment (cont) La.t40 8 -1.16E+OI (6 16) 2B S.13E+oo (2/2) S.13E+oo (2/2) 0 (pCilkg dry) (.6.72E+Ol - S.04E+01) 1.6 rei NNE (-3.32E*OI 1.06E+OI) (-3.32B-Ol 1.06E+OI) Ra*226 8 2.29E+03 (6 16) 2B 2.88E+03 (2/2) 2.88E+03 (212) 0 (I.99E+03 - 2.60B+03) 1.6 rei NNE (1.99E+03 - 3.76E+03) (1.99E+03 - 3.76E+03) TIl-228 8 2.60E+03 (6/6) LTAW 3.39E+03 (2/2) 3.llE+03 (2/2) 0'" (1. 14B+03 - 3. 6lE+03) an site NE-ESB (3.J6E+03
- 3.6IE+03) (1.29E+03
- 4.92E+03)
Ground Water OammaSpec (pCiII) K-40 36 7.50&01 (24/24) 252 3.50E+oo (12 112) -1.ooE+OI (12/12) 0 (-3.tOE+OI - 4.S0E+01) 0.9 rei NNE (-3.1 OE+O 1 - 4.S0E+01) (-3.80E+OI
- 9.ooE+OO) i*
Mn-S4 '36 15 -S.25E-Ot (24/24) 12F3 ' 7.7SE-02 (12/12) 7.7SE-02 (12/ i2) 0 (-2.30E+oo
- 2.50E+OO) S.2 mi WSW (-2.10E+oo
- 2.30E+oo) (-2.10E+OO
- 2.30E+OO)
Co-58 36 IS -6.54E-OI (24/24) 12F3 4.17E-Ol (12/12) 4.17E-OI (12/12) . 0 (-3.80E+oo I.SOE+OO) 5.2 mi WSW (-4.ooE-OI 2.IOE+00) (-4.ooE-OI
- 2.lOE+oo)
Fe-S9 36 30 1.38E-OI (24/24) 4S4 4.50E-OI (12/12) *1.70E+OO (12/12) 0 (-S.10E+00 6.lOE+00) O.S mi ENE (-S.tOEtoo 6.lOEtoo) (-l.30EtOI 2.30EtOO) Co-60 36 IS O.ooE+oo (24124) 12F3 2.4SE-Ol . (12/12) 2ASE*OI (12/12) 0 (-2.20E+oo - 2.40E+00) 5.2 mi WSW (-2.20E+oo
- 2.30E+00) (.2.20E+00 - 2.300+00)
Zn-6S 36 30 .2.SSE+00 (24/24) 12F3 -4.17E-02 (12 112) -4.17E-02 (12/12) 0 (-l.08E+01 - 7.S0E+OO) 5.2 mi WSW (-l.01E+Ol 5.10E+OO) , (-2.20E+00 - 5.10E+00) Zr-9S 36 30 *t.88E-OI (24/24) 454 7.50E-02 (12112) -6.42E-Ol (12 fl2) 0 (-S.80Etoo
- 4.70E+OO) 0.5 .mi ENE I (4.40Etoo - 4.70E+oo) (-S.50E+00
- 4.40E+OO)
Nb-95 36 IS -1.96E-OI (24124) (4.90E+oo - 3.ooE+00) 4S4 0.5 mi ENE j
. 3.33E*02 (12/12)
(-2ooE+oo
- 3.ooE+00)
-S.08E*OI (12/12)
(-2.40E+oo - 2.00E+oo) 0 CS-I34 36 IS 2.46E-01 (24124) 4S4 l.09E+oo (12112) S.5lE-OI (12/12) 0 (-2.50E+oo
- 3.90E+oo) 0.5 mi ENE. (.1.60B+oo - 3.90E+OO) (-3.20EtOO - 2.30E+00) 0*10
TAOLEG TAOLEG
SUMMARY
SUMMARY
OF OF DATA DATA FOR FOR SSES SSES OPERATIONAL RADIOLOGICAL OPERATIONAL RADIOLOGICAL ENVIRONMENTAL ENVIRONMENTAL MONITORING MONITORING PROGRAM* 2004 2004 NAME OF NAME OF FACILITY: FACILITY: SUSQUEHANNA SUSQUEHANNA STEAMSTEAM ELECTRIC ELECTRIC STATION STATION LOCATIONOFFACILlTY: LU"lERNECOUNTY,PENNSYLVANIA LOCATIONOFFACILlTY: LU"lERNECOUNTY,PENNSYLVANIA Reporting l'eriod: Reporting l'eriod: December 29, December 2003 29, 2003 to to January 26. January 200S
- 26. 200S l'age8or13 l'age8or13 ANALYSIS AND ANALYSIS AND LOWERUMIT LOWERUMIT NUMBER OF NUMBER OF MEDIUM MEDIUM OROR PA PATUWA TUWA Y Y TOTAL NUMBER TOTAL NUMBER OF OF ALL lNDlCATOR ALL lNDlCATOR LOCA LOCAnONS nONS LOCAnON LOCA nON WmllllGllEST WmllllGllEST MEAN MEAN CONTROL LOCAnON CONTROL LOCA nON NONROUTINE NONROUTINE SAMPLED SAMPLED OF ANALYSES OF ANALYSES DETECTION DETECTION MEAN (3)
MEAN (3) NAME NAME MEAN (3) MEAN (3) MEAN (3) MEAN (3) RBI'ORTED RBI'ORTED
!UNIT OF MEASUREMr:.N!l PERFORMED!'! !UD!!2! RANGE DISTANCE AND DIREC'TlON RANGE RANGE MEASUREMENTS!4!
Ground Water (cont) Cs-131 36 18 -1.61E-Ol (24/24) 4S4 2.00E-OI (12/12) -2.50E-Ol (12/12) 0 (pCill) (-2.608+00 - 2.308+00) 0.5 mi EN8 (-1.508+00 . 1.908+OO) (-2.20E+OO - 2.008+00) 03-140 36 60 2.088-02 (24/24) 252 4.25E-Ol (12/12) 1.50E-02 (12/12) 0 (-3.008+00 3.908+00) 0.9 mi NN8 (-3.008+00 3.908+00) (*2.508+00 3.806+00) 1..:1*140 36 15 *3.338-02 (24/24) 252 5.088*01 (12 1 12) 9.116-02 (12/12) 0 (-3.408+00 4.508+OO) 0.9 mi NNE (-3.408+00 4.508+OO) (-2.908+00 4.408+(0) H-3 36 2000 4.858+01 (24/24) 4S4 1.618+01 (12 112) 1.958+01 (12/12) 0 (-4.43E+01 1.23E+02) 0.5 mi ENE (-2.568+00 . 1.238+02) (*5.908+01 1.288+02) Air Particulates GrossBCla 312 10 1.398+01 (208 1208) 12EI 1.42E+OI (52/52) 1.30E+OI (104 11(4) 0 (8-03 pCilm3) (3.5IE+OO . 3.66E+Ol) 4.1 mi WSW (6.468+00 3.66E+Ol) (4.42E+00 . 2.298+01) Air Iodine 1-131 312 70 3.818-02 (208 12OS) 1251 3.368-01 (52/52) -3.708*02 (104 11(4) 0 (8-03 pCilm3) (-8.17E+OO 6.808+00) 0.4 mi WSW (*8.136+00 5.236+(0) (*8.138+00 . 6.766+00) Air I'articulates Gamma Spec Quarterly Composite Be-7 24 9.168+01 (16 116) 12E1 9.546+01 (4/4) 8.798+01 (S/S) 0 (6-03 pCilm3) (5.68E+Ol 1.326+02) 4.1 mi WSW (8.316+01 1.166+02) (7.31E+OI I.09E+02) K-40 24 .I.OSE+OO (16/16) 3S2 1.61E+OO (4/4) 1.3IE+OO (S 18) 0 (-I.34E+01 1.756+00) 0.5 mi NE (-1.886+00 1.756+(0) (-6.86E+00 7.596+(0) Mn*S4 24 3.886-02 (16/16) 12EI 1.318-01 (4/4) 1.70E-02 (8/8) 0 (*2.306-01 2.646-01) 4.1 mi WSW (3.736-02 2.64E-OI) (-1.43E-OI 1.38E-Ol) a*1I (
( (" C" TABLEG TABLEG
SUMMARY
SUMMARY
OF OF DATA DATA FORFOR SSES SSES OPERATIONAL RADIOLOGICAL OPERATIONAL RADIOLOGICAL ENVIRONMENTAL ENVIRONMENTAL MONITORING MONITORING PROGRAM* 2004 2004 NAMEOFFACILITY: SUSQUEIIANNA NAMEOFFACILITY: SUSQUEIIANNA STF.AMELECTRIC STF.AMELECTRIC STATIONSTATION LOCATION OF LOCATION OF FACILITY: FACILITY: LUZERNE COUNTY, PENNSYLVANIA LUZERNE COUNTY, PENNSYLVANIA Repot1lng Period: Repot1lng Period: Dl'C'ember 29, Dl'C'ember 29, 2003 2003 to to January 26, January 26, 200S 200S Page 9 Page 9 of.3 of.3 ANALYSIS AND ANALYSIS AND LOWERUMlT LOWERUMlT NmmEROF NmmEROF MEDttJMORPATIIWAY MEDttJMORPATIIWAY TarALNmmER TarALNmmER OF OF AlL INDICATOR AlL INDICATOR LOCATIONS LOCATIONS LOCATION wrmmGHEST MBAN LOCATION wrmmGHEST MBAN CONfROLLOCATION CONfROLLOCATION NONROtmNB NONROtmNB SA.\fl'I.El) SA.\fl'I.El) OF ANALYSES OF ANALYSES DIITECIlON DIITECIlON MBAN(3) MBAN(3) NMffi NMffi "" MEAN(3) MEAN(3) tffiAN(3) tffiAN(3) RBroRTIID RBroRTIID (UNIT OFMEASUREMEN1) (UNIT PERFORMED ~ll OFMEASUREMEN1) PERFORMED (llDl!2) (llDl!2) RANOB RANOB DISTANCE AND DISTANCE AND DlRECI10N DlRECI10N RANOB RANOB RANGE RANGE MBASURl!MENI"S~4! Air Pat1lctdntts (cont) Quarterly Composite Co-58 24 4.20B*02 (16/16) 12Bl t.62B*Ol (4/4) 3.67B*02 (fl/ 8) 0 (B*OJ pCtIm3) (*3.78B-0l
- 3.73B-0l) 4.7 mi WSW (-1.93B-Ol - 3.73E.Ql) (*3.28B-Ol
- 3.32B-OI)
Fe-59 24 *7.87B*02 (16/16) 12B! 7.&)E*Ot (4/4) -4.36B-Ot (8/8) 0 (.2.43B+00
- 1.48B+00) 4.7 mi WSW (3.23B*Ol
- 1) (-t.S9B+oo
- 1.00B+00)
CO-:60 24 4.9SB*02 (161 16) 12Bl IA9B*Ot (4/4) 4.54E*02 (SI8) 0 (-9.91B-02
- 4.ooE-0I) 4.7 mi WSW (9.60B*02 - 2. 19B*OI) (*1.2GB*OJ - 2.92B-Ol) iri-6S 24 -4.63E-Ol (16/16) SOl 9.84B*02 (4/4) .2.49B*Ot (S/8) 0
(-t.96B+00
- 1.39B-OI) 12 mi SSB (-3.56B-OI - 3.8gB.OI) (-l.23B+oo
- 3.8gB.OI) 2'i~9S' 24 -6.76B-02 (16/16) 1151 1.66B-OI (4/4) 8.05B-02 (8/8) 0
(*S.SlB.Ql
- 4.74B-Ol) 004 rot WSW (-1.47B-02
- 4.22B-Ot) '(.3. 15E*Ol
- S.3 lB*O1)
Nb-95 24 7.69B-02 (16 1 16) 1151 1.43B-Ot (4/4) 1.06B.0I (8/S) 0 (-3.10B*Ot .. S.33B*Ol) 0.4 mi WSW (.2.63B.OJ - 4.20B*Ol) (-2.9SB*Ol - 3.07B-0l) Cs-I34 24 SO 7.69E*02 (16/16) Sot 3.85E-02 (4/4) .1.07B*Ol (8/8) 0 (-7.79E*01 - 1.79B*0l) 12 mi SSE (-1.59B*01 - 2.50B*OI) (-8.27B*Ot
- 2.50B*01)
Cs*137. 24 60 3.5SB-02 (16/t6) 115t 1.40E*Ot (4/4) -4.33E-02 (S /8) 0 (-t.74E*OI
- 3.76B.Ol) 0.4 mi WSW (-7.16B~02
- 3.7GB-OI) (.1.89E-01
- 5.19E-02)
Ba-140 24 5.4GE+00 (16/16) 3S2 7.SSE+00 (4/4) 2.6SB-0I (8 IS) 0 (-1.S2B+Ol
- 2.29E+01) O.S mi NB (-l.44B+oo
- 1.97B+0l) (-3.53E+0l
- 2.S4E+Ol)
La-140 24 -g.80B-Ot (16 116) 1151 2.33E+00 (4/4) -3.06B*OJ (11/11) 0 (-1.36B+Ol
- 9.06B+00) 0.4 mi WSW (-6.9tE-Ot - S.24B+OO) (-l.S8B+01
- I.S3E+01)
Q*12
TABLEG TABLEG
SUMMARY
SUMMARY
OF OF DATA DATA FORSSES FORSSES OPERATIONAL RADIOLOGICAL OPERATIONAL RADIOLOGICAL ENVIRONMENTAL ENVIRONMENTAL MONITORlr-;G MONITORlr-;G PROGRAM PROGRAM -- 20042004 NAME OF NAME OF FACILITY: FACILITY: SUSQUEHANNA SUSQUEHANNA STEAM STEAM ELECTRIC ELECTRIC STATION STATION LOCATION OF LOCATION OF FACILITY: FACILITY: LUZERNE LUZERNE COUNTY. COUNTY. PENNSYLVANIA PENNSYLVANIA Rellorting Period: Rellorting Period: December 29, December 29, 2003 2003 to to January 26, January 26, 200S 200S l'age 10 l'age of 13 10 of 13 ANALYSIS AND ANALYSIS AND LOWERIlMlT LOWERIlMlT NUMBER OF NUMBER OF MEDIUMORPATIIWAY MEDIUMORPATIIWAY TOfALNmmER TOfALNmmER OF OF All. INDICATOR All. INDICATOR LOCATIONS LOCATIONS LOCATIONwrrnmGllBSTMEAN LOCATIONwrrnmGllBSTMEAN CONTROL LOCATION CONTROL LOCATION NONROUTINB NONROUTINB SAMPLED SAMPLED OF ANALYSES OF ANALYSES Dl!TEcnON Dl!TEcnON MEAN (3) MEAN (3) NAME NAME MEAN (3) MEAN (3) MBAN(3) MBAN(3) RBl'ORTED RBl'ORTED (UNIT OP (UNIT OP MBMUREM!§!:!!:! MBMUREM!§!:!!:! PERFORMED! PERFORMED! Il Il (llD) (2) (llD) (2) RANGE RANGE nIsrANCB nIsr ANCB M'I) nIRECTlON M'I) nIRECTlON RANGE RANGE RANGB RANGB MBA.'iUREMENf~4~ Milk Milk 1-131 1-131 72 72 4.59E-03 (54/54) 4.59E-03 (54/54) 12B2 12B2 5.39E-02 (19/19) 5.39E-02 (19/19) 1.46E-02 (18 1.46E-02 (18 118) 00 (pCiJl) (-9.ooB-01 5.40B-Ol) 1.7 mi WSW (-1.9OB-Ol - 5.40E-Ol) (-2.70E-01 - 3.9OE-OI) OanunaSpec K-40 76 1.40E+03 (57 157) lOGI 1.45E+03 (19/19) 1.45E+03 (19 I 19) 0 (1.15E+03 1.57E+03) 14 mi SSW (1.28E+03 - 1.62E+03) (I.28E+03 - 1.62E+03) Mn-54 76 -9.41£-02 (57/57) 12B2 -3.68B-02 (19/19) -1.42E+00 (19/19) 0 (-3.50E+00 - 4.20E+OO) 1.7 mi WSW (-3.50E+00 2.20E+00) (-7.70E+00 3.70E+00) Co-58 16 -1. llE-01 (57/57) IOGI 9.47E*02 (19/19) 9.47E-02 (19/19) 0 (-3.70E+00 - 5.IOE+00) 14 mi SSW (-2.60E+oo 3.50E+oo) (-2.60E+oo - 3.50E+00) Fe-59 76 8.72E-OI (57/57) IOGI 2. 18E+00 (19/19) 2. 18E+00 (19/19) 0 (-&.ooE+OO 1.40E+Ol) 14 mi SSW (-2.ooE+oo 1.00£+01) (-2.ooE+oo - 1.00£+01) Co-60 76 1.72E-Ol (57/57) 12B2 6.47E-Ol (19/19) .2.89E-01 (19/19) 0 (-4.10E+00 . 4.10E+00) 1.7 mi WSW (*3.70E+00 . 4.10E+00) (*3.30E+00 - 3.50E+00) Zn-65 76 -1.02E+00 (57/57) toOl 5.42E*Ol (19/19) *8.95E-Ol (19/19) 0 (-1.22E+OI 1.30£+01) 3 mi SSW (-1.22£+01 1.10£+01) (-9.ooE+00 - 1.00£+01) Zr*95 76 -6. 16B-01 (57/57) 1002 1.42E*Ol (19/19) -9.32E-Ol (19/19) 0 (-7.20E+00 8.90£+00) 3.1 mi SSW (-5.50£+00 . 6.50E+00) (-5.50E+00 - 3.20£+00) Nb-95 76 -2.54E-Ol (57 157) 1001 5.26E-03 (19/19) -2.95£-01 (19 J 19) 0 (-5.10E+OO 6.00£+00) 3 mi SSW (-5.IOe+00 6.00£+00) (-3.20E+00 - 3.70£+00) Cs*l34 76 15 1.46£*01 (57/57) 10D2 4.OSE-Ol (19/19) 3.16£-02 (19/19) 0 (-3.80E+.00 3.60£+00) 3.1 mi SSW (-3.40E+00 - 3.40E+00) (*2.30£+00 - 2.40£+00) Cs-137 76 18 -1.09E*Ol (57/57) 1001 3.37E-Ol (19/19) 1.00£-01 (19/19) 0 (-5.10£+00 - 4.10£+00) 3 mi SSW (-1.30E+00 3.60£+00) (-3.60E+00 - 4.50E+00) Ba-140 76 60 2.63£.02 (57/57) 1001 6.58E-Ol (19/19) 1.74£-01 (19119) 0 (-4.20E+00 - 5.00£+00) 3 mi SSW (-3.00£+00 - 2.70E+00) (-3.70E+00 - 2.90E+oo) La-140 76 15 3.33E-02 (57/57) 1001 7.58£-01 (19/19) 2. 16E-OI (19/19) 0 (-4.80£+00 - *5.10E+OO) 3 mi SSW (*3.40£+00 3.10£+00) (-4.30E+00 - 3.30E+00) ( c. c.
(. (00 C' TABLEG TABLEG
SUMMARY
SUMMARY
OF OF DATA DATA FORFOR SSES SSES OPERATIONAL RADIOLOGICAL OPERATIONAL RADIOLOGICAL ENVIRONMENTAL ENVIRONMENTAL MONITORING MONITORING PROGRAM* 2004 2004 NAME OF NAME OF FACILITY: FACILITY: SUSQUEHANNA SUSQUEHANNA STEAM STEAM ELECTRIC ELECTRIC STATION STATION LOCATION OF LOCATION OF FACILITY: FACILITY: LUZERNE LUZERNE COUNTY,COUNTY, PENNSYLVANIA PENNSYLVANIA Reporting Period: Reporting Period: Det'ember 29, 2003 Det'ember 29, 2003 10 10 January 26, 2005 January 26, 2005 Page 11 Page 11 oft3 oft3 ANALYSIS AND ANALYSIS AND LOWER LOWER UMlT UMlT NUMBER OF NUMBER OF MEDIUM MEDIUM OROR PATIIWAY PATIIWAY TOfALNUMDER TOfALNUMDER OF OF AlLlNDJCATOR LOCATIONS AlLlNDJCATOR LOCATIONS LOC'ATIONWrrnmGHESTMBAN LOC'ATIONWrrnmGHESTMBAN CONTROLLOC'ATION CONTROLLOC'ATION NONROU1lNE NONROU1lNE SAMPLED SAMPLED OF ANALYSES OF ANALYSES DrrrncnoN DrrrncnoN MEAN (3) MEAN (3) NAME NAME MEAN 0) MEAN 0) MEAN (3) MEAN (3) Rl!PORTED Rl!PORTED (UNlTOFMEASUREMENn PERFORMED~ll (UNlTOFMEASUREMENn CUD~~2) RANGE RANGE DISTANCI! AND DISTANCI! AND DIRECITON DIRECITON RANGE RANGE RANGE RANGE 4l MEASURI!M1!NrS~4l Soil Gamma Spec (pCilkg dry) K-40 8 1.45E+04 (6/6) 1386 1.73E+04 (2/2) 9.27E+03 (2/2) 0 (I.20E+04 1.8SE+(4) 0.4 mi W (1.60E+04 1.8SE+04) (8.14E+03 l.04E+04) Mn-S4 R 1.10E+01 (6/6) 13S6 1.80E+OI (2/2) -1.IOE+Ol (2/2) o~ (-4.ooE+oo - 2.ooE+01) 0.4 00 W (1.70E+OI I.90E+Ol) (-230E+OI U)OE+oo) " Co-58 8 -I.02E+OI (6/6) 1281 -6.00E+00 (2/2) -2.45E+OI (2/2) 0 (-2.60E+Ol . O.ooE+oo) 0.4 00 WSW (-8.ooE+00 * -4.ooE+oo) (-2.90E+Ol * *2.ooE+Ol) Fe-59 8 6.ooE+00 (6/6) 1386 2.35E+Ol (2/2) -230E+Ol (2/2) 0 (-3.50E+Ol . 6.20E+01) 0.4 00 W (-1.50E+01
- 6.20E+01) (-4.500+01 .1.ooE+OO)
Co-60 8 5. 17E+00 (6/6) 382 l.ooE+OI (2/2) 250E+00 (2/2) 0 (-1.20E+Ol I.S0E+Ol) O.S 00 NE (6.ooE+00
- 1.40E+01) (-1.ooE+oo
- 6.ooE+00)
Zn-6S 8 2.48E+01 (616) 80! 9.IOE+0I (2/2) 9. 1OE+Ol (2/2) 0 (-4.10E+Ol - 7.ooE+01) 12 mi SSE (8.ooE+OI
- t.02E+0z) (8.ooE+Ol
- 1.00E+02)
Zr-95 8 -299E+03 (6/6) 801 255E+OI (2/2) 255E+OI (2/2) 0 (-8.30E+03 -2ooE+01) 12 mi SSE (l.ooE+Ol - 4.10E+01) (1.ooE+OI - 4.10E+01) Nb-95 8 -5.50E+00 (616) 1281 9.ooE+00 (2/2) -2.50E+00 (2/2) o* (-260E+Ol 1.70E+Ol) 0.4 00 WSW (l.ooB+oo - 1.70E+Ol) (-1.70E+0I 1.20E+0I) Cs-l34 g 1.23E+Ol (6/6) 1281 4.35E+Ol (2/2) -1.95E+Ol (2/2) 0 (-3.ooE+Ol 6.40E+Ol) 0.4 00 WSW (2.30E+Ol 6.40E+Ol) (-3.S0E+OI -l.ooE+oo) Cs-137 g 273E+OI (6/6) gOt 1. llE+02 (2/2) 1.1IE+02 (2/2) 0 (-1.50E+Ol 7.60E+Ol) 12 .00 SSE I (7.80E+Ol
- 1.43E+02) (7.80E+Ot 1.43E+02)
Ba*140 8 6.33B+ot (6/6) 3SZ 1.30E+02 (2/2) 250E+01 (2/2) 0 (-8.00E+01 - 250E+02) 0.5 00 NE, (1.ooE+Ol - 250E+02) (*5.ooE+01 1.008+02) La* 140 8 -5.17E+OO (6/6) 801 1.20E+Ol (2/2) 1.20E+OI (2/2) 0 (-2408+01 3.008+01) 12 00 SSE. (l.ooE+OI - 1.40E+01) (l.ooE+Ol 1.40E+OI)
TADLEG TADLEG
SUMMARY
SUMMARY
OF OF DATA DATA FORFOR SSES SSES OPERATIONAL RADIOLOGICAL OPERATIONAL RADIOLOGICAL ENVIRONMENTAL ENVIRONMENTAL MONITORING MONITORING PROGRAM* 2004 2004 NAME 01<' NAME FACILITY: SUSQUEHANNA 01<' FACILITY: SUSQUEHANNA STEAM STEAM ELECTRIC ELECTRIC STATION STATION LOCATION OF LOCATION OF FACILITY: FACILITY: LUZERNE COUNTY, PENNSYLVANIA LUZERNE COUNTY, PENNSYLVANIA Reporting Period: Reporting Period: December 29, 1003 December 29, 1003 to to Jalluary 26, Jalluary 26, 2005 2005 I'age 12 I'age 12 of of 13 13 ANALYSIS AND ANALYSIS AND LOWERUMIT LOWERUMIT NmmEROF NmmEROF MEDIUM ORPATllWAY TOTALNmmER MEDIUM ORPATllWAY TOTALNmmER OF OF AIL INDICATOR AIL INDICATOR LOCATIONS LOCATIONS LOCATION WITn LOCATION WITn InGlIESTMBAN InGlIESTMBAN CONt'ROLLOCATION CONt'ROLLOCATION NONROUI1NE NONROUI1NE SAMl'LED SAMl'LED OF ANALYSES OF ANALYSES DE.TF.CUON DE.TF.CUON MEAN (3) MEAN (3) NAME NAME MBAN(3) MBAN(3) MnAN(3) MnAN(3) REPORTED REPORTED (UNIT OPMBA (UNIT OPMBA...... IIREMENn IIREMENn PERFORMED PERFORMED !Il
!Il (Un~(2) RANGE RANGE D1SfANCE AND D1SfANCE AND DIREcrlON DIREcrlON RANGE RANGE RANGE RANGE MBASUREMENTg4!
MBASUREMENTg4! Soil Soil (com) Ra*226 0 0 (pCilkg dry) TIl*228 8 9. 89E+02 (6/6) 13S6 1. 15E+03 (212) 7.07E+02 (2/2) 0 0.70E+02 - . 1.18E+03) 0.4 mi W (1. llE+03 1. 18E+03) (6.44E+02 7.70E+02) Food/Garden Crops GaIJUna Spec (pCiIkg weI) De-7 -2.70E+Ol (1/1) 12F7 .2.70E.Ol (I I) 0 (*2.70E+OI - -2. 70E+OI) 8.3 mi WSW (-2.70E+Ol -2.70E+Ol) K-40 3.95E+03 (1/1) 12F1 3.95E+03 (l I I) 0 (3.95E+03 - 3.95E+03) 8.3 mi WSW (3.95E+03 - 3.95E+03) Mn:-54 2.22E+00 (1/1) 12F1 2.22E+00 (1/1) 0 (2.22E+00 2.22E+00) 8.3 mi WSW (2.22E+00 - 2.22E+00) Co-58 4.83E*Ol (Ill) 12F1 4.83E*Ol (1 11) 0 (4.83E-01 - 4.83E*01) 8.3 mi WSW (4.83E*Ol - 4.83E*01) Fe-59 -2.22E+00 (Ill) 12F1 -2.22E+OO (111) 0 (*2.22E+00 - -2.22E+OO) 8.3 mi WSW (-2.22E+00 - -2.22E+OO) Co-60 1.46E+00 (111) 12F1 1.46E+00 (1 11) 0 (1.46E+OO 1.46E+00) 8.3 mi WSW (l.46£+00 1.46£+00) Zu-65 *1.48E+OI (1 II) 12F1 -1.48E+OI (III) 0 (-1.48E+OI -1.48£+01) 8.3 mi WSW (-1.48£+01 - -1.48£+01) Zr*95 2.79£+00 (1/1) 12F1 2.79£+00 (1 11) 0 (2.79E+00 2.79E+00) 8.3 mi WSW (2.79E+00 - 2.79£+00) Nb-95 8.93E+00 (Ill) 12F1 8.93E+00 (111) 0 (8.93E+00 8.93E+00) 8.3 mi WSW (8.93£+00 - 8.93E+00) 1-131 -1.35E+Ol (Ill) 12F1 -1.35£+01 (l/1) 0 (-1.35E+Ol - -1.35£+01) 8.3 mi WSW (-1.35£+01 . -1.35£+01) ( c.,
"TADLEG "TADLEG
SUMMARY
SUMMARY
OF OF DATA DATA FOR FOR SSES SSES OPERATIONAL RADIOLOGICAL OPERATIONAL RADIOLOGICAL ENVIRONMENTAL ENVIRONMENTAL MONITORINGMONITORING PROGRAM.PROGRAM. 2004 2004 NAME OF NAME OF FACILITY: FACILITY: SUSQUEHANNA SUSQUEHANNA STEAM STEAM ELECTRIC ELECTRIC STATION STATION LOCATIONOFFACILlTY: LUZERNE LOCATIONOFFACILlTY: LUZERNE COUNTY, COUNTY, PENNSYLVANIA PENNSYLVANIA Reportin2 Period: Reportin2 Period: December 29, December 29, 2003 2003 to to January 26, January 26, 2005 2005 Pllge 13 Pllge or 13 13 or 13 ANALYSIS AND ANALYSIS AND LOWERUMIT LOWERUMIT NUMBER OF NUMBER OF ORPAnIWAY MEDIUM ORPAnIWAY MEDIUM Tar ALNUMBER TarALNUMBER OF OF AIL INDICATOR AIL INDICATOR LOCATIONS LOCATIONS LOCATIONWrmInGHP.sTMEAN LOCATIONWrmInGHP.sTMEAN CONTROL LOCATION CONTROL LOCATION NONROUI'lNB NONROUI'lNB SAMI'LED SAMI'LED OF ANALYSES OF ANALYSES DlrrEcnON DlrrEcnON MEAN (3) MEAN (3) NAME .. NAME MEAN (3) MEAN (3) ~mAN(3) REroRTED REroRTED (UNITOFl>mASUREMENf) (UNITOFl>mASUREMENf) PERFORMED~l} (llD!(2~ RANGB RANGB DISTANCB AND DISTANCB AND DIREcnON DIREcnON RANGB RANGB RANGB RANGB MEASUREMENTS(4) MEASUREMENTS(4) FoO!lIGnrclen Crops (cont) (pCiJkg wet) Cs-l34 -1.09E+Ol (1/1) 12F7 *1.09E+Ol (l/l) 0 (*I.09E+Ol -1.09E+OI) 8.3 rni WSW (.I.09E+OI -1.09E+Ol) Cs-t37 *6.33E*Ol (1/1) 12F7 -6.33E*Ol (1/1) 0 (-6.33E-Ol -6.33E*Ol) 8.3 rni WSW (*6.33E*Ol -6.33E*Ol) Ba-140 2.59E+Ol (I 11) 12F7 2.59E+OI (Ill) 0 (2.S9E+0I 2.S9E+Ol) 8.3 mi WSW (2.S9E+OI 2.59E+Ol) La* 140 -4.53E-01 (l/l) 12F7 -4.53E-Ol (I II) 0 (-4.S3E-Ol -4.S3E*0l) 8.3 rni WSW (-4.S3E-OI -4.S3E.Ol) The total I. The I. total number number ofof analyses analyses does does not not include include duplicates. duplicates. splits. splits. or or repeated repeated analyses. analyses.
- 2. The Teclmical
- 2. The Teclmical Requirement LLD's are Requirement LLD's shown when are shown when applicable.
applicable.
- 3. The means
- 3. The means are are based on all based on all available available measured measured results. When possible.
results. When this includes possible. this includes those those below the MDC! below the MDC! asas well as those well as above them. those above them.
- 4. USNRC
- 4. USNRC reporting levels arc reporting levels arc specified in the specified in the Technical Requirements.
Technical Requirements.
u
- j THE FOLLOWING THREE THE FOLLOWING THREE PAGES PAGES ARE CORRECTIONS ARE CORRECTIONS TO TO THE THE
*2000,2002,2003 ANNUAL RADIOLOGICAL ANNUAL RADIOLOGICAL ENVIRONMENTAL OPERATING ENVIRONMENTAL OPERATING REPORTS -- APPENDIX REPORTS APPENDIX GG I
\J
C" ( C TADLEG TADLEG
SUMMARY
SUMMARY
OF OF DATA DATA FOR FOR SSES SSES OPERATIONAL RADIOLOGICAL OPERATIONAL RADIOLOGICAL ENVIRONMENTAL ENVIRONMENTAL MONITORING MONITORING PROGRAM* 2000 2000 NAME NAME OF OF FACILITY: FACILITY: SUSQUEHANNA SUSQUEHANNA STEAM STEAM ELECTRIC ELECTRIC STATION STATION LOCATION OF LOCATION OF FACILITY: FACILITY: LUZERNE LUZERNE COUNTY, COUNTY, PENNSYLVANIA PENNSYLVANIA Reporting Period: Reporting Period: Dec:ember 28, Dec:ember 28, 1999 1999 to to January 17,2001 January 17,2001 P8geRor13 P8geRor13 ANALYSIS AND ANALYSIS LOWER LIMIT AND LOWER LIMIT NUM13EROF NUM13EROF l-ffiDIDMOR PATIIWAY TOTALNUMDER l-ffiDIDMOR PATIIWAY TOTALNUMDER OF OF AU INDICATOR AU INDICATOR LOCATIONS LOCATIONS LOCATION WmnnGJIEST LOCATION WmnnGJIEST MEANMEAN CONTROL LOCATION CONTROL LOCATION NONROtmN'B NONROtmN'B SAMPLED SAMPLED OPANAlYSES OPANAlYSES DETECTION DETECTION MEAN 0) MEAN 0) NMm NMm MEAN (3) MEAN (3) MEAN (3) MEAN (3) REPORTED REPORTED ~IT OF OF MEASUREMENT) MEASUREMENT) PERFORMED !1} PERFORMED !1} Q:LD Q: l!2l LDl!2l RANGE RANGE Dl'ST ANCE AND Dl'STANCE AND DIRECTION DIRECTION RANGB RANGB RANGE RANGE MEASUREMENTS(41 MEASUREMENTS(41 Ground Water (cont) Cs-137 49 18 I.34E+OO (39) 282 . 1.56E+OO (10) 1.22E+OO (10) 0 (pCi/I) (-1.40E+00 - 4.40E+OO) 0.9 mi NNE (-1.20E+OO - 4.25E...oo) (-1.20E+OO- 4.82E+OO) Ba-140 48 60 -3.30E-OJ (39) 484 2.48E...oo (JO) 6.11E-OI (9) 0 (-8.80E+Ol - 2.35E+(1) 0.5 mi ENE (-1.00E+Ol - 2.35E+Ol) (-9.50E+OO - 1.10E+Ol) La-140 49 15 -9.47E-Ol (39) 4S5 2.92E+OO (9) -3.33E+OO (10) 0 (-3.11E+Ol - 8.70E+OO) 0.5 mi ENE (-3.00E+OO* 8.70E+OO) (-1.908+01 - 3.50E+OO) H-3 60 2000 4.54E+Ol (48) 484 8.60E+Ol (12) 2.80E+Ol (12) 0 (-5.96E+Ol- 2.05E+02) 0.5 mi ENE (O'{)()E+OO - 2.05E+(2) (-5.94E+01 - 9.65E+Ol) Air P8rticulate~ Omss Bem 520 JO 1.47E+Ol (416) 584 1.78E+Ol (52) l.31E+Ol (104) 0 (E-03 pCi/m3) (1.00E+OO - 1.90E+o2) 0.8 mi E (5.40E+OO - 1.90E+(2) (4.60E+OO - 2.80E+(1) Air Jndine 1-131 399 70 -2.92E+OO (319) 10S3 -1.52E+OO (40) -3.32E+OO (80) 0 (8-03 pCi/m3) (-8.9GE+Ol - 5.80E+OO) 0.6 mi SSW (-3.51E+Ol - 3.50E+OO) (.8.29E+01 - 5.00E+00) Air PflrtiClllate~ Gamma Spec Quarterly Composite Be..7 39 8.84E+Ol (31) 3S2 9.36E+Ol (4) 8.22E+Ol (8) 0 (E-03 pCi/m3) (6.22E+Ol - I.25E+02) 0.5 mi NE (7.47E+Ol - l.t9E+(2) (5.85E+Ol- 1.00E+(2) K40 30 1.43E+OO (24) 13S6 9.08E+00 (3) 3.7GE+OO (6) 0 (-9.50E+OO - 2.$08+01) 0.4 mi W (*2.10B-OI - 2.50E+(1) (-3.00E+OO - 2.80E+01) Mn-$4 30 1.59E-02 (24) 601 5.608-02 (3) 4.83E-02 (6) 0 (-1.20E-Ol - 1.50E-Ol) 13.$ mi ESE (2.90E 9.90E-02) (.1.80E 9.908-02) CORRECTION TO CORRECTION TO 2000 2000 APPENDIX APPENDIX G G 0*10
C" c* ( TA8LEG TA8LEG
SUMMARY
SUMMARY
OF OF DATA DATA FOR FOR SSF..8 SSF..8 OPF.RATIONAL OPF.RA TIONAL RADIOLOGICAL RADIOLOGICAL ENVIRONMENTAL ENVIRONMENTAL MONITORING MONITORING PROGRAM* 2002 2002 NAME OF NAME OF FACILITY: FACILITY: SUSQUEIIANNA SUSQUEIIANNA STEAMSTEAM ELECTRIC ELECTRIC STATION STATION I,OCATION OF I,OCATION OF FACILITY: FACILITY: LUZERNF. LUZERNF. COUNTY. COUNTY. PENNSYINANIA PENNSYINANIA Period: R~portlng Period: December 26,2001 December 26,2001 to to January 2003 31, 2003 January 31, Page8of13 Page8of13 ANAL.YSIS ANAL.YSIS AND AND LOWERUMIT LOWERUMIT NUMBER OF NUMBER OF MEDIUM MEDIUM OR OR PATHWAY PATHWAY TOTAL NUMBER TOTAL NUMBER OF OF AlL INDICATOR AlL INDICATOR LOCATIONS LOCATIONS LOCATION wml LOCATION wml InGHFSTMEAN InGHFSTMEAN CONTROL LOCA CONTROL LOCAnON nON NONROtJ11NE NONROtJ11NE SAMrLEO SAMrLEO OF ANALYSES OF ANALYSES DETECTION DETECTION MEAN (3) MEAN (3) NAME NAME l'vfEAN(3} l'vfEAN(3} MEAN(3} MEAN(3} REPORTED REPORTED
~IT OF OF Mr>ASUREMr::!m Mr>ASUREMr::!m rERFORMED C1}
rERFORMED C1} <U.D)f2}
<U.D)f2} RANGE RANGE DlSTANCE AND DlSTANCE AND DIRECTION DIRECTION RANGE RANGE RANGE RANGE l'vfEASUREMENTS!41 l'vfEASUREMENTS!41 Ground Water (cont) Cs*137 36 18 -S.08B-01 (24/24) 282 -1.7513*01 (12/12) -5.0013*01 (12/12) 0 (pCill) (-2.50E-f.00 1.7013+(0) 0.9 mi NNE (-1.20E+OO 1.70E+00) (-2.6013+00 2.10E+OO) 83-140 36 60 -5.0013*02 (24/24) 128 1.1513+00 (12 I 12) 1.1513+00 (12/12) 0
(-7.30E+OO 4.3013+00) 5.2 mi WSW (-1.80E+OO . 3.80E-f.00) (-1.80B+OO 3.80E-f.00) La*140 36 IS -5.83B-02 (24/24) 128 1.3313+00 (12 I 12) J.33B+OO (121 J2) 0 (-8.40E+OO 4.90E+00) 5.2 mi WSW (-2.ooE+OO 4.4013+(0) (-2.ooE+OO . 4.4013+(0) H*3 36 2000 7.7713+01 (24/24) 484 1.1713+02 (12/12) 6.2613+01 (121 J2) 0 (-6.292+01 2.832+02) 0.5 mi ENE (0.002+00 - 2.83E+02) (-4.212+01 2.072+02) . Air Particulates Gross Deta 306 10 1.562+01 (204/204) 382 Ui62+0t (SI 151) 1.362+01 (102 1102) 0 (13*03 pCi/m3) (1.0013+00 3.0413+01) 0.5 mi NE (6.60E+OO - 3.0013+01) (5.ooB-01 2.692+01) Air Iodine 1*131 318 70 2.23B-0I (521212) 601 6.60B-01 (13 153) 4.42B-Ol (26 I 1(6) 0 (B-03 pCUm3) (-4.6713+00 1.0113+01) 13.5 mi ESE (-1.9613+00 - 6.992+00) (-2.0813+00 6.9913+00) Air Particulates Gamma Spec Quarterly Composite De-7 24 1.3713+02 (16/16) 1356 2.5713+02 (4/4) 9.37E+Ol (8/8) 0 (13*03 pCi/ml) (1.0013+01 7.2813+02) 0.4 mi W (9.1713+01 7.288+02) (7.5413+01 1.2313+02) K-40 24 -7.60E-02 (4 I 16) 13S6 9.2913+00 (1/4) 1.50E+00 (3/8) 0 (-8.31E-f.00 9.2913+00) 0.4 mi W (9.29E+00 - 9.29E+OO) (2.16E-OI 2.8613+(0) Mn*54 24 I.SSE-OI (4/16) 12S1 3.28&01 (1/4) -8.9813-02 (2/8) 0 (4.25B-02 3.28B-OJ) 0.4 mi WSW (3.28B-01 3.28B-0I) (-1.3713-01 -4.26B-02) CORRECTION TO CORRECTION TO 20022002 APPENDIX APPENDIX G G G-I
c c TABLEG TABLEG C
SUMMARY
SUMMARY
OF OF DATA DATA FORSSES FORSSES OPERATIONAL RADIOLOGICAL OPERATIONAL RADIOLOGICAL ENVIRONMENTAL ENVIRONMENTAL MONITORING MONITORING PROGRAM* 2003 2003 NAME OF NAME OF FACILITY: FACILITY: SUSQUEHANNA SUSQUEHANNA STEAMSTEAM ELECTRIC ELECTRIC STATION STATION LOCATIONOFFACILITY: LUZERNECOUNTY,PF.NNSYLVANJA LOCATIONOFFACILITY: LUZERNECOUNTY,PF.NNSYLVANJA Reporting Period: Reporting Period: D<<embcr 30, D<<embcr 30, 2002 2002 to to January 30, January 30, 2004 2004 Page8ofJ3 Page8ofJ3 ANALYSIS AND ANALYSIS AND LOWER LIMIT LOWER LIMIT NUM8EROF NUM8EROF MEDIUM MEDIUM OR OR PATIIWAY PATIIWAY TOTALNUM8ER TOTALNUM8ER OF OF AU. INDICATOR AU. INDICATOR LOCATIONS LOCATIONS LOCATION wml LOCATION wml JII0lJF.ST JII0lJF.ST MEAN MEAN CONTROL LOCATION CONTROL LOCATION NONROUTlNE NONROUTlNE SAMM.ED SAMM.ED OF ANALYSES OF ANALYSES DIITECllON DIITECllON MEAN (3) MEAN (3) NAME NAME MEAN (3) MEAN (3) MEAN (3) MEAN (3) REPORTED REPORTED (UNIT OF (UNIT OF MEASUREM!a!!!l MEASUREM!a!!!l PERFORMED (l! PERFORMED (l! (W))G,2 (W))G,2 RANGE RANGE DISTANCE AND DISTANCE AND DIRECTION DIRECTION RANGE RANGE RANGE RANGE MEASUREMENTS!....!! MEASUREMENTS! Ground Water (cont) Cs-137 36 18 -1.28B-Ol (24/24) 152 -1.148-01 (12/12) -3.7SE-Ol (12/12) 0 (pCill) (.1.70E-+OO 1.40E+00) 0.9 mi NNE (-1.70E+OO 1.40E+00) (-2.20E+OO 1.20E-+OO) B3-140 36 60 -2.67E-OI (24/24) 454 6.08B-01 (12 112) 1.08E-OI (12 112) 0 (-S.20E-+OO 3.00E-+OO) 0.5 mi ENE (.1.80E+OO - 2.6OE+OO) (-4.80E+OO - 5.108+(0) La-t40 36 IS . *2.96E-01 (24/24) 454 7.00E*Or (12 112) l.lSE*OJ (12/12) 0 (.6.00E+OO - 3.40E-+OO) 0.5 mi ENE (.2. I OE+OO - 3.00E+OO) (*5.508+00 5.80E+OO) H-3 36 2000 S.44E+OI (24/24) 4S4 8.438+01 (12 112) 1.74E+0I (12/12) 0 (-6.74E+01 1.938+(2) 0.5 ml ENB (-2.46B+00 - 1.93E+(2) (-8.84E+o1 8.86E+OI) AII' Particulates Gross Beta 312 10 1.46E+Ot (208 /208) 352 t.5IB+01 (52' 52) 1.348+01 (104 1104) 0 (B-03 pCi/m3) (3.59E-+OO - 3.17E+(1) 0.5 ml NE (4.9IB+OO .- 3.02E+01) (3.16E+OO - 3.IOE+OI) AII' Iodine 1*131 312 70 6.OlB-Ot (208/208) 352 8.29B-0I (52/52) -6.44E-02 (104 1104) 0 (E-03 pCi/m3) (-5.27E+OO 5.97E+OO) 0.5 mi NE (-2.79B+OO 4.59E+00) (-3.748+00 6.30E+OO) AII' Particulates Gamma Spec Quarterly Composite De-7 24 9.06E+01 (16/16) 12S1 9.t OE+O 1 (4/4) S.2 IE+O I (8/S) 0 (E-03 pCi/m3) (6.70E+01 I.IlE+02) 0.4 mi WSW (7.65E+0l . 1.06E+02) (6.63E+0l 9.34E+01) K-40 24 1.298-+00 (16 116) 352 2.21E+OO (4' 4) 9.20E-Ol (8/8) 0 (-4.94E-+OO 4.04E+(0) O.S mi NE (2.27E-Ol 4.04E+(0) (-5.79E+00 - 4.66E+(0) Mn-S4 24 3.63B-02 (16/}6) 6Gt 1.10B-Ot (4/4) 9.23E-02 (8/8) 0 (-6.98B-02 2.23E-OI) 13.5 mi ESE (-5.75E-02 3.29E-OI) (-5.758-02 3.29E-01) CORRECTION TO CORRECTION TO 2003 2003 APPENDIX APPENDIX G G ()'10
APPENDIXH APPENDIXH II .. 2004 Radiological 2004 Radiological Environmental Environmental Monitoring Monitoring Report Report H*t
.w
.w Appendix H Appendix H The data presented The data presented inin the the following following tabJes tabJes were were included included if if specific specific analysis analysis results results routinely exceeded routinely exceeded the the applicable applicable MDCs MDCs in in 2004 2004 and/or and/or routinely routinely may may have have done done soso in in previous years.
previous years. The The comparisons comparisons maymay be be useful useful for for observing observing any any step step changes changes that that may may . occur occur in in the the environment environment over over aa wide wide area. area. However, However, the the importance importance attached attached to to these these comparisons comparisons should should be tempered by be tempered by the the understanding understanding that that changes changes inin methods methods of of analysis, typical analysis, typical MDCs MDCs achieved achieved byby the the analyses, analyses, and and averaging averaging methods methods over over the the years years may tend may tend to to blur blur the the picture picture in in some some cases. cases. 2004 Radiological 2004 Radiological Environmentall'tJonitoring Environmentall'tJonitoring Report Report H-2 H-2
\.J
Appendix 11 A1\ffiIENT RADIATION A1\ffiIENT RADIATION l\10NITORING l\10NITORING TABLEHI
- ':' A1\ffiIENT A1\ffiIENT RADIATION RADIATION ,LEVELS ,LEVELS AS AS MEASURED MEASURED BY BY TLDS TLDS (mRlSTD (mRlSTD QTR) QTR) ~{
Location Location Indicator Indicator Control Control Period Period Pre-Op Pre-Op Operational Operational Pre-Op Pre-Op Operational Operational 1978-81 1978-81 ' 1982-03 1982-03 2004 2004 1978-81 1978-81 1982-03 1982-03 ,2004
,2004 Range Range 18.5-19.2 18.5-19.2 14.7-20.8 14.7-20.8 -- 15.0-17.9 15.0-17.9 14.8-20.8 14.8-20.8 --
l\fean l\fean 18.9 18.9 18.3 18.3 20.8 20.8 16.3 16.3 18.0 18.0 19.8 19.8 AQUATIC PATHWAY AQUATIC PATHWAY l\fONITORINGl\fONITORING TABLEH2 TABLEH2
.. ' . /"SURFACE
/"SURFACE WATER WATER GROSS'BETA GROSS'BETA ACTIVITIES{pCiIl)'*'*~:.:,~ .... " '-"::
Location Location Indicator Indicator Control Control Period Period Pre-Op Pre-Op Operational Operational Pre-Op , Pre-Op Operational Operational 1978*81 1982-03 1982-03 2004 2004 1978*81 1982-03 1982-03 2004 2004 Ran~e~9 3.0-7.7 3.0-7.7 -- 2.9-5.2 2.9-5.2 2.4-6.7 2.4-6.7 ---- Mean Mean 3.8 3.8 5.6 5.6 5.7 5.7 4.0 4.0 3.7 3.7 2.8 2.8 TABLEH3
",,',SURFACE WATER WATER IODINE IODINE....131 ACTIVITIES (( CiIJ).
131 ACTIVITIES CiIJ). Location Location Indicator Indicator Control
. Control Period' Period' Pre-O Pre-O oo erational erational Pre-O Pre-O o erational o erational 1979*81 1982*03 2004 2004 1979-81 1979-81 1982-03 1982-03 2004 2004 Ran ee Ran 0.24-0.37 0.24-0.37 0.06-0.61 0.06-0.61 Mean Mean 0.29 0.29 0.32 0.32 O.
O.
'TABLEH4 '
SURFACE WATER
,:, . ' 7 ; ' , . ' ~:,' .. SURFACE WATER TRITIUM TRITIUM ACTIVITIESACTIVITIES (pCiIl)
(pCiIl) ~:::. '," " '.'f~!.;:* :.' Location Location Indicator Indicator ; Control Control Period Period Pre*Op Operational
, Operational '. 'Pre-Op
'Pre-Op Operational Operational 1978*81 .'1982-03'!' ,:. 2004 2004 1978-81 1978-81 '1982*03* 2004 2004 Range Range l\lean l\lean 101-122 101-122 109 109 126-1576 126-1576 621 621 1.575 1.575 119-319 119-319 171 171
-239 -+212
-239 -+212 51 51 76 76
**1990 1990 results results werewere not not averaged averaged with with 1982-01 1982-01 data data because because the the validity validity of of the the 1990 values 1990 values is is questionable questionable in in some some instances.
instances. Laboratory Laboratory analysis analysis error error is is suspected. suspected. See See the the 1990 1990 Annual Annual Report. Report. 11*3 2004 Radiological 2004 Radiological Em'ironmental Em'ironmental Monitoring Monitoring ReportReport
Appendix 11 Appendix 11 TABLE TABLE 115115 DRINKING ,WATER DRINKING ,WATER GROSS GROSS ALPHA ALPHA ACTIVITIES ACTIVITIES (pCi/l)~~/:;:;~;~'\.:,**;. Period Period Preoperational Preoperational Operational Operational 1980 -- 81 1980 81 1982-03 1982-03 2004 2004 Ran~e ---- 0.1-10.0 0.1-10.0 ---- l\1ean l\1ean 1.3 1.3 1.3 1.3 0.14 0.14 TABLE TABLE 11 11 66 DRINKING' WATER
.. :..:,' DRINKING' WATER GROSS GROSS nETA.ACTIVITIES*(pCi/lY.i,.j;)*~*, ~:;,(?,: ,
Period Period Preoperational Preoperational Operational Operational 1977 -- 81 1977 81 1982 -- 03 1982 03 2004 2004 Ran~e 2.2 -- 3.2 2.2 3.2 . 2.1 -- 5.4 2.1 5.4 -- Mean Mean 2.7 2.7 3.1 3.1 1.9 1.9 TABLE 11 11 77 DRINKlNG,WATERTRITIUMACTIVITIES'(pCill),>:'.:: .:?/~ . ' Period Period Preoperational Preoperational Operational Operational 1977 -81 1977 -81 1982 -- 03 1982 03 2004 2004 Ranee Ranee 101-194 101-194 -247 -- +220
-247 +220 ----
Mean Mean 132 132 62 62 74 74 TABLEH8 Location Location Indicator Indicator Control Control Period Period Pre-O Pre-O o erational o erational Pre* 00 o o erational erational 1977*81 1982-03 1982-03 2004 2004 1977*81 1982~03. 2004 2004 3.1.- 5.3 3.1.- 5.3 2.8 -- 3.6 2.8 3.6 3.1 -- 4.2 3.1 4.2 3.7 3.7 3.5 3.5 3.2 3.2 3.5 3.5 200~ Radiological Environmental Radiological Environmental Monitoring Monitoring Report Report H*4
Appendix H Appendix H TABLEH*9 SEDIMENT POTASSIUM;40ACTIVITIES
- ,;-C',:' ~.': .:: SEDIMENT POTASSIUM;40ACTIVITIES (pCilg'dry);:.),<,< T,~'j:~,';.,O;;::
Location' Location' Indicator, Indicator, Control Control Period Period Pre-Op Pre-Op Operational :, Operational Pre-Op' Pre-Op' Operational
' , Operational 1978-81 1978-81 1982*03 ,2004
,2004 1978*81 1982*03 2004 2004 Range Range 8.6-10.4 8.6-10.4 7.4-13.6 7.4-13.6 ..---- 7.5-11.0 7.5-11.0 6.2-13.0 6.2-13.0 '.-
Mean Mean 9.3 9.3 10.8 10.8 :: 13.1 13.1 7.7 7.7 10.6 10.6 14.8 14.8 TABLEH10 TABLEH10
" ' ' ' 'SEDIME:ST RADIUM';226
'SEDIME:ST RADIUM';226 ACTIVITIES ACTIVITIES (pCilgdrjrr":,::-: ',':~,::: ,.:', ;
,,~.
Location Location Indicator Indicator Control Control Period Period Pre-Op, Pre-Op, Operational Operational Pre*Op Operational Operational 1978-81 1978-81 1982*03 '2004
'2004 1978*81* 1982-03
' 1982-03 '2004
'2004 Range Range 0.5-0.7 0.5-0.7 0.5-2.4 ;
0.5-2.4 ---- 0.6-1.9 0.6-1.9 0.4-2.1 0.4-2.1 -- Mean 0.6 1.5 2.3 0.7 1.5 2.9 Mean 0.6 1.5 2.3 0.7 1.5 2.9 TABLEH11 TABLEH11 II
' ,:",."<." SE[JIl\1ENTTHORIlM~228ACTIVIT]ES-(pCilgdrYl~::';':~ ,
"~'::::
':-', ':- '0 Location Location Indicator "
Indicator ; ,, Control" Control" Period Period 1984~03*' ,, ':2004
':2004 1984 -- 03*
1984 03* 2004 2004 Range Range no 3.2 no vv ** .,
., 3.2 ---- 0.8 -3.0 0.8 -3.0 ----
Mean Mean 1.2 1.2 2.6 2.6 1.2 1.2 : 3.1 3.1
*Th-232 was
*Th-232 was reported reported instead instead of of Th-228 Th-228 inin 1990.
1990.
'TABLEH 12
, 'TABLEH 12
." ,,:.,,;, '. '" SEDIMENT,CESIUM~137.ACTIVITIES (pCilg dryr;:;~', '., ,::,,, ,- "
Location Location .- " Indicator, ,,: Indicator, .. 'Control
'Control Period Period ' Pre*Op Operational
, Operational Pre-Op Pre-Op Operational Operational 1978-81 1978-81 1982*03 i, ,2004,2004 1978-81 1978-81 1982-03 :2004 1982-03 :2004 Range Range 0.08-0.15 0.08-0.15 0.04-0.17
0.04-0.17 .-
.- 0.08-0.21 0.08-0.21 0.06-0.21 0.06-0.21 ,-
Mean Mean 0.10 0.10 0.08 0.08 0.02 0.02 0.11 0.11 0.11 0.11 0.07 0.07 H*S 2004 RadiologicaJ 2004 RadiologicaJ Environmental Environmental Monitoring Monitoring Report Report
Appendix H ATl\'IOSPHERIC PATHWAY ATl\'IOSPHERIC PATHWAY MONITORING MONITORING TABLEH 13 TABLEH 13 , f
....-..-/
,Location
,Location Indicator Indicator Control Control Period Period Pre-O Pre-O o erational o erational Pre-O Pre-O o erational o erational ,,
1978*81 1982*03 2004 2004 1978*81 1982*03 2004 2004 24-97 24-97 13 -- 28.8 13 28.8 24 -102 24 -102 12-27.7 12-27.7 61 61 16.3 16.3 14 14 62 62 15.5 15.5 13 13 TABLEH 14 AIR}-A'RTf
'~:, '>,~ ,<~ AIR}- A'RTfCULA'TE CULA'TE 'BERyLljth\1.'i
'BERyLljth\1.'i .tcTIVrrn!S pciim3:t:
.tcTIVrrn!S cE~3' pciim3:t: ,, :
Location Location Indicator Indicator " Control Control Period Period Pre-Opi Pre-Opi Operational Operational Pre*Op Operational Operational 1978-81 1978-81 1982*03* 2004 2004 1978*81 1982-03* 1982-03* 2004 2004 Ran2e Ran2e 69 -- 81 69 81 50 -- 137 50 137 ---- 59- 85 59- 85 49 -- 126 49 126 ---- Mean Mean 76 76 95 95 92 92 72 72 88 88 88 88
- 1990 results
*1990 results were were not not averaged 1982-01 data averaged wi~~ 1982-01 data because because the the validity validity of of the the 1990 values 1990 values is is questionable questionable in in some some instances.
instances. Laboratory Laboratory analysis analysis error error is is suspected. See suspected. See the 1990 Annual the 1990 Annual Report. Report. TERRESTRIAL PATHWAY TERRESTRIAL PATHWAY MONITORING MONITORING TABLEH15
.' .. SOIL SOIL POTASSIUM.;40 POTASSIUM.;40 ACTIVITIES ACTIVITIES (pCilg (pCilg dry) dry) "" .. , ~ '!' ~
Location Location Indicator Indicator Control Control Period Period Pre-Op Pre-Op Operational Operational Pre-Op Pre-Op Operational Operational 1979&81 1979&81 1984*03 2004 2004 1979&81 1979&81 1984-03 1984-03 2004 2004
'Range 'Range 9.2 -- 9.7 9.2 9.7 9.4-15.3 9.4-15.3 ---- 9.1-11.0 9.1-11.0 7.4-14.1 7.4-14.1 ----
l\'fean l\'fean 9.5 9.5 11.9 11.9 14.5 14.5 10.1 10.1 10.5 10.5 9.3 9.3 2004 Radiological 2004 Radiological Environmental Environmental Monitoring Monitoring Report Report II*6
Appe1ldix H Appe1ldix H TABLEH 16 TABLEH 16
- ,:::; ~ :;:';~':,,; :, . :: SOIL SOIL RADIUM.;.226 RADIUM.;.226 ACTIVITIES ACTIVITIES (pCilg (pCilg dry)dry) ~'.: ... ' ":: .,": ....: . . ..
Location Location Indicator Indicator Control Control Period Period Pre-Op Pre-Op Operational Operational Pre-Op Pre-Op Operational Operational 1979&81 1979&81 1984~03* 2004* 2004* 1979&81 1979&81 ~ .. :1984-03
- 1984-03 2004 2004 Ranee Ranee 0.8 -1.3 0.8 -1.3 -2.5 0.8 -2.5 0.8 ---- 0.8 -1.2 0.8 -1.2 '1.0 -- 2.2
'1.0 2.2 ----
Mean Mean 1.1 1.1 1.6 1.6 ND ND 1.0 1.0 1.7 1.7 ND ND
** Radium-226 Radium-226 was was not not detected detected (NO)
(NO) inin 2002, 2002, 2003, 2003, oror 2004. 2004. TABLEH17 ACTIVITIES (pCilgdry); (pCilgdry); , ;'.' --: ..
,'. '" . ; ~ .. SOILTIIORIUM~228 ACTIVITIES t _ .'
Location Location Indicator Indicator Control Control Period Period Pre-Op Pre-Op Operational Operational Pre-Op Pre-Op Operational Operational 1979&81 1979&81 1984-03 1984-03 2004 2004 1979&81 1979&81 1984-03 1984-03 2004 2004 Range Range 0.9 -1.3 0.9 -1.3 0.8-2.0 0.8-2.0 ---- ---- 0.7 -- 2.4 0.7 2.4 -- Mean Mean 1.1 1.1 1.6 1.6 ].0
].0 ].0
].0 1.0 1.0 0.7 0.7 TABLEH18
., ...... :.. ( ..:: .. ~ "".: . '" /SOIL*CESIUM.;137 ACTIVITIES ACTIVITIES (pCile'c:lry)' (pCile'c:lry)' ..... .,', :. ....
. ~';, ~:
~'
Location Location Indicator Indicator Control Control Period Period Pre*Op Operational Operational .. Pre-Op Pre-Op Operational Operational 1979&81 1979&81 1982*03 2004 2004 1979&81 1979&81 1982-03 1982-03 2004 2004 Ranee Ranee 0.5 -- 0.7 0.5 0.02 -- 0.45 0.7 0.02 0.45 0.2 -- 1.2 0.2 1.2 0.07 -1.2 0.07 -1.2 Mean Mean 0.6 0.6 0.21 0.21 0.03 0.03 0.7 0.7 0.37 0.37 0.11 0.11 TABLEH 19 TABLEH 19
.. .: :-,' . ;' :***.... l\flLK POTASSIU_\1:~40 ACTIVITIESACTIVITIES (,)CiIJ),. (,)CiIJ),. .. -:~.:. ):' "; , '
Location Location Indicator Indicator Control Control Period Period Pre-Op Pre-Op Operational Operational Pre-Op Pre-Op Operational Operational 1978-81 1978-81 1985-03 .. 2004 1985-03 2004 1978-81 1978-81 1985-03 1985-03 2004 2004 Ranee Ranee 1222-1500 1241-1422 1222-1500 1241-1422 ---- 1273-1500 1247-1472 1273-1500 1247-1472 ---- Mean Mean 1325 1325 1335.2 1335.2 1401 1401 1390 1390 1334.7 1334.7 1455 1455 H*' 2004 Radiological
. 2004 Radiological Environmental Environmental Monitoring Monitoring Report Report
AppendixH TABLE H20
,', ~-;.-- '-. GROUNDWATERTRJiTIUM GROUNDWATERTRJiTIUM ACTIVITIES ACTIVITIES (CiII)~';-
Location Location Indicator Indicator Control Control Period Period Pre*O '0 erational
'0 erational oo erational-erational-1980*81 1982*03 2004 2004 1982*03 2004 2004 94*109 -206
-206 -- +180
+180 117-119 117-119 -206 -+260
-206 -+260 101 101 58.6 58.6 49 49 118 118 65.1 65.1 20 20 2004 Radiological 2004 Radiological Environmental Environmental Monitoring Monitoring Report Report H*8
" I *
... I:.
I:. APPENDIX II APPENDIX FSPECiFiG;,ANArYSfSfREsilliTSj:ABifLWfED~BY3~. r:~~;'~~!'~~}~~i:~,~~8:'~MEDIA~wND~;S*MBLIN;G':~:PERi6D\*}~~ti~:{(i1~t:f~:.~,,(1. ~~tt;t~~;oa.~.,.,. __ ~: __ ~~.~.... ,,~",,"," ... ~J.'_::'~;' ,. ___~""t..._~ . .____, " . ..-.._..~:.~:;~~.:r~::~!;;::[J.: t -
. , ; .. ~ .:"" l, * "
. I'.,
2004 Radiological 2004 Radiological Environmental Environmental Monitoring Monitoring ReportReport 1*1
Appendixl Results Results of of analyses analyses are are generally generally reported reported in in the the following following tables tables to to two two significant significant figures. Random figures. Random uncertainties uncertainties of of counting counting are are reported reported to to the the same same decimal decimal placeplace as as the the result. result. Calculated values for Calculated values for analysis analysis results results are are reported reported withwith the the random random uncertainty uncertainty of of counting at counting at two two standard standard deviations (2S), determined deviations (2S), determined by by considering considering both both thethe sample sample and background and background count count rates. The uncertainty rates. The uncertainty of of an an activity activity is is influenced influenced by by the the volume volume or mass or mass of of the the sample, sample, the the background background countcount rate, rate, the the count count times, times, thethe method method usedused toto round off round off the the value value obtained obtained to to reflect reflect its its degree degree of of significance. significance. and and other other factors. factors. The The uncertainties of uncertainties of activities activities determined determined by by gamma gamma spectrometric spectrometric analyses analyses areare also also influenced by influenced by the the relative relative concentrations concentrations of of the the radionuclides radionuclides in in the the sample, sample, the the energies energies and intensities and intensities of of the the gammas gammas emitted emitted by by those those radionuclides, radionuclides, and and the the assumptions assumptions used used in selecting in selecting the the radionuclides radionuclides to to be be quantitatively quantitatively determined. determined. . . - . Results Results reported reported as as less less than <<) in than <<) in these these tables tables are are below below thethe minimum minimum detectable detectable concentrations (MDCs). concentrations (MDCs). The MOCis an The MOCis an estimate estimate of of the the dete~tion capabilities capabilities of of the the overall measurement overall measurement method, method, taking taking into into account account not not only only the the counting counting system, system, but but also also the characteristics the characteristics of of the the sample sample being being counted. counted. When When the MOC is the MOC is used used asas the the level level to to decide whether decide whether or or not not to to enter enter aa measured measured value value into into aa table, table, there there isis aa 50% 50% chance chance that that the value the value will will bebe entered entered when when thethe actual actual sample sample activity activity isis equivalent equivalent to to the the MOC. MOC. There is There is only only aa five five percent percent chance chance that that aa value value representing representing aa fluctuation fluctuation in in background background activity will activity will bebe entered entered as as sample sample activity activity in in such such anan instance. instance. Measured values Measured values for for the the activities of specific activities of specific radionuclides, radionuclides, such such as as the the man-made man-made gamma-emitting radionucJides beryllium-7 gamma-emitting radionucJides beryllium-7 and and cesium-137, cesium-137, only only appear appear in in the the following tables following tables forfor each each specific specific medium medium when when thethe levels levels that that are are measured measured exceedexceed thethe MOe values MOe values for for those those measurements measurements and and those those radionuclides radionuclides are are actually actually identified identified as as present in present in the the samples. samples. Measured Measured values values forfor the the analyses analyses thatthat are are not not radionucIide radionucIide specific, such specific, such asas gross gross alpha alpha andand beta beta analyses, analyses, alsoalso are are presented presented in in the the tables tables forfor specific media specific media onlyonly when when the the levels levels that that are are measured measured actually actually exceed exceed thethe MOCs. MOCs. 2004 Radiological 2004 Radiological Environmental Environmental Monitoring Monitoring Report Report 1-2 1-2
(' c' TARLE 1*1 TARLE c* , ENVIRONMENTAL TIIERMOLUMINESCENT DOSIMETRY ENVIRONMENTAL TIIERMOLUMINESCENT DOSIMETRY RESULTS RESULTS SUSQUEHANNA STEAM SUSQUEHANNA STEAM ELECTRIC ELECTRIC STATION* 2004 2004 Results (1) Results are in (1) are in mRlstd. mRlstd. qtr qtr (2) +/- 2S (2) +/- 2S (3) (3) First Quarter First Quarter Second Quarter Second Quarter ThIrd Quarter ThIrd Quarter Fourth Quarter Fourth Quarter 01/27/04 01/27/04 toto 04/23/04 04/23/04 04/21/04 to to 07/21/04 07/21/04 07/20104 07/20104 to to 10/27/04 10/27/04 10/26/04 10/26/04 toto 01/26/05 I.ocation I.ocation ONSITE ONSITE 152 152 21.7 21.7 :t:t 1.3 1.3 24.2 24.2 :t :t 1.2 1.2 23.7 23.7 :t:t 2.12.1 25.9 25.9 :t:t 0.80.8 252 252 18.1 :f:: 18.1 1.7
- f:: 1.7 20.0 :f::
20.0 :f:: 1.5 1.5 18.0 :f:: 18.0 1.7
- f:: 1.7 22.3 :f::
22.3 :f:: 1.6 1.6 253 253 19.8 :f:: 19.8 0.9
- f:: 0.9 21.5 :f::
21.5 1.4
- f:: 1.4 21.2 :f::
21.2 1.4
- f:: 1.4 24.4 :f::
24.4 2.2
- f:: 2.2 352 352 18.0 :f::
18.0 0.9
- f:: 0.9 17.6 :f::
17.6 2.2
- f:: 2.2 16.7 :f::
16.7 1.0
- f:: 1.0 19.3 :f::
19.3 1.0
- f:: 1.0 353 353 17.9 :f::
17.9 0.9
- f:: 0.9 17.7 :f::
17.7 :f:: 1.21.2 15.2 :f:: 15.2 1.8
- f:: 1.8 19.5 :f::
19.5 1.2
- f:: 1.2 354 354 17.7 :f::
17.7 0.4
- f:: 0.4 (8)
(8) (8) (8) (8) (8) 453 453 22.8 :f:: 22.8 0.6
- f:: 0.6 21.8 21.8 :!:
- !: 1.6 1.6 21.8 ::I:
21.8 1.7
- I: 1.7 25.1 25.1 ::I:
- I: 2.4 2.4 456 456 18.5 ::I:
18.5 1.3
- I: 1.3 17.9 17.9 :!:
- !: 0.6 0.6 16.0 :f::
16.0 2.3
- f:: 2.3 20.5 20.5 :f::
- f:: 0.8 0.8 554 554 16.6 ::I:
16.6 0.9
- I: 0.9 16.7 16.7 :!:
- !: 1.0 1.0 15.7 :f::
15.7 1.6
- f:: 1.6 18.6 18.6 :!:
- !: 1.6 1.6 557 557 17.6 ::I:
17.6 0.9
- I: 0.9 18.0 18.0 :!:
- !: 1.6 1.6 16.5 ::I:
16.5 0.7
- I: 0.7 19.0 19.0 ::I:
- I: 2.0 2.0 6S4 6S4 25.9 ::I:
25.9 1.7
- I: 1.7 26.9 26.9 :I:
- I: 2.2 2.2 25.1, ::!:
25.1, 1.7
- !: 1.7 28.5 28.5 :I:
- I: 1.6 1.6 659 659 24.7 ::I:
24.7 1.1
- I: 1.1 25.4 25.4 ::t:
- t: 2.6 2.6 25.0 ;;I:
25.0 2.0
;;I: 2.0 28.7 28.7 ::t:
- t: 2.2 2.2
.7S6 .7S6 24.9 ::t:
24.9 0.9
- t: 0.9 26.0 26.0 ::t:
- t: 3.4 3.4 24.0 ;;I:
24.0 2.0
;;I: 2.0 28.0 28.0 ::I:
- I: 1.6 1.6 7S7 7S7 18.7 ::I:
18.7 1.7
- I: 1.7 18.6 18.6 ::t:
- t: 1.0 1.0 16.3 ::!:
16.3 1.6
- !: 1.6 19.4 19.4 ::t:
- t: 1.0 1.0 8S2 8S2 25.0 ::t:
25.0 0.9
- t: 0.9 25.4 25.4 ::t:
- t: 2.2 2.2 23.7 ;;I:
23.7 1.3
;;I: 1.3 27.1 27.1 ::t:
- t: 2.6 2.6 9S2 9S2 42.8 ::t:
42.8 2.8
- t: 2.8 43.8 43.8 ::I:
- I: 4.3 4.3 44.7 ::I:
44.7 3.3
- I: 3.3 51.0 51.0 ::!:
- !: 5.6 5.6 10S1 10S1 18.4 ::!:
18.4 0.4
- !: 0.4 17.4 17.4 ::!:
- !: 1.0 1.0 16.1 ::!:
16.1 2.0
- !: 2.0 19.6 19.6 ::!:
- !: 0.8 0.8 10S2 10S2 31.8 ::!:
31.8 2.8
- !: 2.8 31.8 31.8 ::!:
- !: 2.6 2.6 30.7 ::!:
30.7 2.5
- !: 2.5 34.4 34.4 +/-
+/- 2.8 2.8 10S3 10S3 17.5 :t 17.5 1.3
- t 1.3 (8)
(8) (8) (8) (8) (8) 11S3 11S3 27.5 ::!: 27.5 2.1
- !: 2.1 27.3 27.3 ::!:
- !: 1.8 1.8 25.7 :!:
25.7 1.4
- !: 1.4 28.6 28.6 +/- 1.6
+/- 1.6 11S7 11S7 20.0 ::!:
20.0 0.9
- !: 0.9 19.2 19.2 ::!:
- !: 1.4 1.4 18.7 :t 18.7 1.4
- t 1.4 21.3 21.3 +/- 2.0
+/- 2.0
(*3
TABLEI*l ENVIRONMENTAL TIlERMOLUMINESCENT DOSIMETRY ENVIRONMENTAL TIlERMOLUMINESCENT DOSIMETRY RESULTSRESULTS SUSQUEHANNA STEAM SUSQUEHANNA STEAM ELECTRIC ELECTRIC STATION* 2004 2004 Results (1) Results are in (1) are in mRlstd. mRlstd. qtr qtr (2) +/- 2S (2) +/- 2S (3) (3) First Quarter First Quarter 5econd Quarter 5econd Quarter Third Quarter Third Quarter Fourth Quarter Fourth Quarter 01/27/04 to to 04/23104 04121/04 to to 07/21/04 07/20/04 to to 10/27/04 10/27/04 10126/04 toto 01/26/05 01/26/05 J.ocation J.ocation 1251 1251 20.3 20.3 +/- 1.3
+/- 1.3 20.4 20.4 :t 1.6
- t 1.6 18.5 18.5 :t 1.5
- t 1.5 21.6 21.6 :t 1.2
- t 1.2 1253 1253 24.9 24.9 1.3
+/- 1.3
+/- 26.2 :t 26.2 :t 2.0 2.0 22.6 +/-
22.6 +/- 2.2 2.2 26.0 +/- 26.0 +/- 1.2 1.2 1254 1254 25.9 25.9 +/- 1.7
+/- 1.7 (8)
(8) (8) (8) (8) (8) 1255 1255 22.3 22.3 0.6
+/- 0.6
+/- (8)
(8) (8) (8) (8) (8) 12S6 12S6 22.5 22.5 :t
- t 1.5 1.5 (8)
(8) (8) (8) (8) (8) 12S7 12S7 17.9 17.9 :t
- t 1.3 1.3 17.1 17.1 :t 1.0
- t 1.0 15.8 15.8 +/- 1.3
+/- 1.3 18.3 18.3 +/- 2.2
+/- 2.2 1352 1352 25.9 25.9 +/-
+/- 3.2 3.2 24.0 +/-
24.0 +/- 1.2 1.2 23.8 23.8 3.3
+/- 3.3
+/- 27.8 +/-
27.8 +/- 2.0 2.0 1354 1354 24.0 24.0 +/-
+/- 1.9 1.9 (8)
(8) (8) (8) (8) (8) 1355 1355 25.7 25.7 +/-
+/- 2.1 2.1 24.4 24.4 +/- 2.4
+/- 2.4 24.5 24.5 2.4
+/- 2.4
+/- 27.5 27.5 +/- 2.4
+/- 2.4 13S6 13S6 22.2 22.2 +/-
+/- 1.5 1.5 22.2 22.2 2.2
+/- 2.2
+/- 21.8 21.8 1.8
+/- 1.8
+/- 25.0 25.0 +/- 1.4
+/- 1.4 1455 1455 22.9 22.9 +/-
+/- 1.1 1.1 22.3 22.3 3.0
+/- 3.0
+/- 20.4 20.4 1.2
+/- 1.2
+/- 23.7 23.7 +/- 0.8
+/- 0.8 1456 1456 21.3 21.3 +/-
+/- 1.3 1.3 (8)
(8) (8) (8) (8) (8) 1555 1555 19.4 19.4 +/-
+/- 1.7 1.7 20.1 20.1 +/- 1.0
+/- 1.0 19.3 19.3 +/- 1.5
+/- 1.5 21.7 21.7 1.6
+/- 1.6
+/-
1651 1651 20.5 20.5 +/-
+/- 1.1 1.1 23.4 23.4 3.0
+/- 3.0
+/- 22.2 +/-
22.2 +/- 1.5 1.5 24.4 24.4 +/- 1.2
+/- 1.2 1652 1652 22.9 22.9 +/-
+/- 1.7 1.7 23.3 23.3 +/- 0.4
+/- 0.4 22.9 +/-
22.9 1.6
+/- 1.6 26.1 26.1 :t
- t 0.8 0.8 See the See the comments comments atat the the end end of of this this table.
table. 1-4 1-4 ( (
(' 0,. ( TAlu....E TAlu E 1*1 c. ENVIRONMENTAL TIIERMOLUMINESCENT ENVIRONMENTAL TIIERMOLUMINESCENT DOSIMETRY DOSIMETRY RESULTSRESULTS SUSQUEHANNA STEAM SUSQUEHANNA STEAM ELECTRIC ELECTRIC STATION* 2004 2004 Results (l) Results are in (l) are in mRlstd. mRlstd. qtr qtr (2) +/- 2S (2) +/- 2S (3) (3) First Quarter First Quarter Second Quarter Second Quarter Third Quarter Third Quarter Fourth Quarter Fourth Quarter 01/27/04 01/27/04 to to 04/23/04 04/23/04 04/21/04 04/21/04 to to 07/21/04 07/21/04 07/20/04 07/20/04 to to 10/27/04 10/27/04 10/26/04 10/26/04 to to 01/26/05 01/26/05 Location Location MILE OFFSITE 0*1 MILE OFFSITE 6A4 6A4 21.7 21.7 +/- 0.6
+/- 0.6 20.5 20.5 +/- 1.0
+/- 1.0 18.7 18.7 +/- 1.8
+/- 1.8 22.4 22.4 +/- 1.6
+/- 1.6 BA3 BA3 IS.5 IS.5 :t 1.5
- t 1.5 17.4 :t 17.4 :t 1.0 1.0 16.2 :t 16.2 :t 1.3 1.3 19.7 19.7 :t 1.4
- t 1.4 15A3 15A3 18.9 18.9 0.9
- t 0.9
- t (4)
(4) IS.3 +/- IS.3 1.7
+/- 1.7 21.S 21.S +/- 1.1
+/- 1.1 16A2 16A2 16.3 16.3 +/- 1.3
+/- 1.3 17.1 +/-
17.1 1.0
+/- 1.0 (4)
(4) 18.5 18.5 1.2
+/- 1.2
+/-
MILE..C:; OFFSITE 1*2 MILE..C:; OFFSITE 1B1 1B1 18.9 18.9 +/-+/- 0.9 0.9 (8) (8) (8) (8) (8) (8) 283 283 1.1 19.0*:!: 1.1 (8) (8) (8) (8) (8) (8) 2B4 2B4 :!: 1.9 19.5 :!: 19.5 1.9 .. (8) (8) . (8) (8) (8) (8) 583 . 583 17.9 :!: 17.9 :!: 0.9 0.9 (8) (8) (8) (8) (8) (8) 782 782 18.6 :!: 18.6 :!: 1.5 1.5 . (8)(8) (8) (8) (8) (8) 8B2 8B2 18.6 :t 18.6 1.5
- t 1.5 17.9 17.9 +/-
+/- 1.01.0 16.6 +/-
16.6 1.5
+/- 1.5 19.7 +/-
19.7 1.0
+/- 1.0 981 981 17.2 1.1
- !: 1.1 17.2 :!: 17.7 17.7 +/- 1.2
+/- 1.2 16.0 +/-
16.0 +/- 1.3 1.3 18.8 +/- 18.8 +/- 1.4 1.4 10B2 10B2 14.6 +/- 14.6 +/- 1.71.7 (8) (8) (8) (8) (8) (8) 10B3 10B3 18.4 +/- 18.4 +/- 1.31.3 17.5 17.5 +/- 1.2
+/- 1.2 15.7 15.7 +/-+/- 0.7 0.7 18.8 +/-
18.8 1.2
+/- 1.2 10B4 10B4 20.1 +/-
20.1 +/- 2.4 2.4 (8) (8) (8) (8) (8) (8) 12B4 12B4 18.6 +/- 18.6 +/- 0.6 0.6 (8) (8) (8) (8) (8) (8) 13B1-13B1- 18.0 +/- 18.0 +/- 1.51.5 (8) (8) (8) (8) (8) (8) 14B3 14B3 19.0 :t 19.0 0.6
- t 0.6 (8)
(8) (8) (8) (8) (8) 15B1 15B1 18.1 +/- 18.1 0.9
+/- 0.9 (8)
(8) (8) (8) (8) (8) 1682 1682 17.2 +/- 17.2 +/- 1.1 1.1 (8) (8) (8) (8) .. (8) (8) MILES OFFSITE 2*3 MILES OFFSITE 11C1 11C1 21.1 +/- 21.1 +/- 2.1 2.1 (8) (8) (8) (8) (8) (8) See the See the comments comments at at the the end end of of this this table. table. I*S
TABLE 1*1 TABLE ENVIRONMENTAL TIIERMOLUMINESCENT DOSIMETRY ENVIRONMENTAL TIIERMOLUMINESCENT DOSIMETRY RESULTS RESULTS SUSQUEHANNA STEAM SUSQUEHANNA STEAM ELECTRIC ELECTRIC STATION* 2004 2004 Results (1) Results are in (1) are in mRlstd. mRlstd. qtr +/- 2S (2) +/- qtr (2) 2S (3) (3) First Quarter First Quarter Second Quarter Second Quarter third Quarter third Quarter Fourth Quarter Fourth Quarter 01/27/04 01/27/04 to to 04/23104 04/23104 04/21/04 04/21/04 to to 07/21/04 07/21/04 07/20/04 07/20/04 to to 10/27/04 10/27/04 10126/04 10126/04 toto 01/26/05 01/26/05 J.ocation J.ocation 3-4 MILES 3-4 MILES OFFSITR OFFSITR 105 105 21.1 21.1 +/- 0.9
+/- 0.9 20.3 20.3 2.0
+/- 2.0
+/- 18.9 18.9 1.7
+/- 1.7
+/- (S)
(S) 601 601 22.3 22.3 2.2
+/- 2.2
+/- (8)
(8) (8) (8) (8) (8) 803 803 19.8 19.8 +/- 1.5
+/- 1.5 19.4 19.4 +/- 1.4
+/- 1.4 .. 17.6 17.6 1.3
+/- 1.3
+/- 20.9 20.9 +/- 1.6
+/- 1.6 904 904 20.7 20.7 +/- 1.3
+/- 1.3 20.2 20.2 +/- 1.4
+/- 1.4 18.2 18.2 1.2
+/- 1.2
+/- 21.4 21.4 2.6
+/- 2.6
+/-
1001 1001 20.4 20.4 +/- 0.9
+/- 0.9 18.6 18.6 2.0
+/- 2.0
+/- 17.6 17.6 +/- 1.7
+/- 1.7 21.0 21.0 +/- 1.2
+/- 1.2 1202 1202 21.0 21.0 +/- 1.7
+/- 1.7 (4)
(4) 19.3 19.3 1.8
+/- 1.8
+/- 22.2 22.2 2.0
+/- 2.0
+/-
1401 1401 19.1 19.1 +/- 1.5
+/- 1.5 20.3 20.3 +/- 1.2
+/- 1.2 18.2 18.2 1.0
+/- 1.0
+/- 21.2 21.2 1.2
+/- 1.2
+/-
4-5 MILES 4-5 MILES OFFSITR OFFSITR 3E1 3E1 17.9 17.9 +/-
+/- 1.8 1.8 16.6 16.6 +/- 1.2
+/- 1.2 14.9 14.9 +/- 0.7
+/- 0.7 18.7 18.7 +/-
+/- 0.4 0.4 4E2 4E2 21.3 21.3 +/-
+/- 0.9 0.9 19.7 19.7 +/- 1.2
+/- 1.2 18.8 18.8 1.9
+/- 1.9
+/- 21.0 21.0 +/-
+/- 1.0 1.0 5E2 5E2 20.3 20.3 +/-
+/- 1.8 1.8 18.9 18.9 +/- 1.4
+/- 1.4 17.7 17.7 1.0
+/- 1.0
+/- 21.8 21.8 +/-
+/- 2.6 2.6 6E1 6E1 22.S 22.S +/-
+/- 1.3 1.3 20.7 20.7 1.6
+/- 1.6
+/- 20.1 20.1 +/- 1.3
+/- 1.3 23.4 23.4 +/-
+/- 1.8 1.8 7El 7El 20.9 20.9 +/-
+/- 2.4 2.4 19.2 19.2 1.8
+/- 1.8
+/- 18.1 18.1 +/- 1.6
+/- 1.6 21.6 21.6 1.6
+/- 1.6
+/-
l1E1 l1E1 17.6 17.6 +/- 1.3
+/- 1.3 17.2 17.2 1.2
+/- 1.2
+/- IS.0 IS.0 1.4
+/- 1.4
+/- (S)
(S) 12E1 12E1 18.0 18.0 +/- 0.9
+/- 0.9 18.1 18.1 +/- 2.3
+/- 2.3 16.3 16.3 1.3
+/- 1.3
+/- 19.4 19.4 +/- 0.8
+/- 0.8 13E4 13E4 21.6 21.6 +/- 1.7
+/- 1.7 21.S 21.S 1.0
+/- 1.0
+/- 19.5 19.5 +/- 2.5
+/- 2.5 23.2 23.2 2.0
+/- 2.0
+/-
MILK" O 5*10 MILK" O ......
......SITE SITE 2F1 2F1 19.1 19.1 0.9
+/- 0.9
+/- 19.2 19.2 +/- 1.4
+/- 1.4 17.4 17.4 +/- 1.4
+/- 1.4 20.6 20.6 +/- 1.6
+/- 1.6 8F2 8F2 18.5 18.5 1.3
+/- 1.3
+/- (8)
(8) (8) (8) (8) (8) 12F2 12F2 20.0 20.0 1.3
+/- 1.3
+/- (8)
(8) (8) (8) (8) (8) 15F1 15F1 20.0 20.0 1.7
+/- 1.7
+/- 20.7 +/-
20.7 +/- 1.5 1.5 19.1 +/- 19.1 +/- 1.3 1.3 21.8 +/- 21.8 +/- 1.0 1.0 16F1 16F1 21.1 21.1 +/- 2.1
+/- 2.1 21.9 +/-
21.9 0.6
+/- 0.6 19.6 +/-
19.6 1.8
+/- 1.8 22.5 +/-
22.5 1.5
+/- 1.5 See the See the comments comments at at the the end end of of this table.
this table. 1*6
- c. c (
ENVIRONMENTAL ENVIRONMENTAL TIIERMOLUMINESCENT T(~LEI-l TIIERMOLUMINESCENT DOSIMETRY DOSIMETRY RESULTS RESULTS SUSQUEHANNA STEAM SUSQUEHANNA STEAM ELECTRIC ELECTRIC STATION* 2004 2004 Results (1) Results are in (1) are in mRlstd. mRlstd. qtr qtr (2) (2) +/-+/- 2S 2S (3) (3) First Quarter First Quarter Second Quarter Second Quarter Third Quarter Third Quarter Fourth Quarter Fourth Quarter 01127104 to 01127104 04123/04 to 04123/04 04121104 to 04121104 07121/04 to 07121/04 07120104 to 07120104 10/27104 to 10/27104 10/26/04 to 10/26/04 01/26/05 to 01/26/05 Location Location MILES 10*20 MILES 3G4 3G4 21.2 21.2 +/-
+/- 2.0 2.0 20.0 20.0 +/- 1.6
+/- 1.6 19.3 19.3 +/- 1.2
+/- 1.2 23.5 23.5 +/- 2.0
+/- 2.0 4G1 4G1 22.8 22.8 +/-
+/- 2.2 2.2 21.1 +/-
21.1 +/- 1.8 1.8 19.3 +/- 19.3 +/- 1.3 1.3 23.6 +/- 23.6 +/- 1.0 1.0 6G1 6G1 22.2 22.2 +/-
+/- 1.1 1.1 (8)
(8) (8) (8) (8) (8) 7G1 7G1 18.9 18.9 +/-
+/- 1.1 1.1 18.4 +/-
18.4 1.6
+/- 1.6 17.3 +/-
17.3 1.4
+/- 1.4 21.0 +/-
21.0 1.4
+/- 1.4 7G2 7G2 18.9 18.9 +/-
+/- 1.1 1.1 (8)
(8) (8) (8) (8) (8) 8G1 8G1 17.2 17.2 +/-
+/- 1.3 1.3 (8)
(8) (8) (8) (8) (8) 12G1 12G1 17.5 17.5 +/-
+/- 0.9 0.9 17.9 +/-
17.9 1.0
+/- 1.0 16.0 +/-
16.0 0.5
+/- 0.5 .. 18.9 18.9 +/- 1.8
+/- 1.8 12G4 12G4 20.7 20.7 +/-
+/- 1.3 1.3 20.2 20.2 +/- +/- 0.6 0.6 19.3 19.3 +/- +/- 2.3 2.3 22.1 +/-
22.1 +/- 1.4 1.4 See the See the comments comments at at the the end end of of this this table. table. Location Location Indicator Indicator Average (6) Average (6) 20.8 +/- 20.8 12.8
+/- 12.8 21.2 +/-
21.2 12.6
+/- 12.6 19.9 +/-
19.9 12.3
+/- 12.3 23.2 +/-
23.2 12.6
+/- 12.6 Control Control Average (6)
Average (6) 19.9 +/- 19.9 4.1
+/- 4.1 19.5 +/-
19.5 3.1
+/- 3.1 18.2 +/-
18.2 3.3
+/- 3.3 21.8 +/-
21.8 3.5
+/- 3.5 COMMENTS COMMENTS (1)
(1) Individual monitor location Individual monitor location results results are are normally normally thethe average average of of the the elemental elemental doses doses ofof six six calcium calcium elements elements fromfrom the the two two TLOs TLOs assigned assigned toto each each monitoring location. monitoring location. (2) (2) A standard A standard (std.) (std.) quarter quarter (qtr.) (qtr.) is is considered considered to to be be 91.25 days. Results 91.25 days. Results obtained obtained for for monitoring monitoring periods periods ofof other other durations durations are are normalized normalized by by multiplying them multiplying them byby 91.25/x. where where xx is is the the actual actual duration duration in days of in days of the the period. period. . (3) (3) Uncertainties for Uncertainties for individual individual monitoring monitoring location location results results are are two two standard standard deviations deviations ofof the the elemental elemental doses doses ofof six six calcium calcium elements elements fromfrom the the two two TLOs assigned TLOs assigned toto each each monitorin monitorin glocation, glocation, representing representing thethe variability variability between between thethe elemental elemental doses doses ofof each each ofof the the six six TLO TLO elements. elements. (4) (4) TLOs were TLOs were not in the not in the field field at at this this monitoring monitoring location location during during this this quarter. quarter. Refer Refer to to Ap.,endix Ap.,endix A A of of this this report report for for an an explanation explanation of of program program changes changes to the to the REMP. REMP. . I (5) (5) No measurement No measurement couldcould be be made made because because the the TLOs TLOs were were lost. lost. stolen stolen oror damaged. damaged. (6) (6) Uncertainties associated Uncertainties associated with with quarterly quarterly indicator indicator andand control control averages averages areare two two standard standard deviations, deviations, representing representing the the variability variability between between the the results results of of the individual the individual monitoring monitoring locations. locations. (7) (7) Oata were Oata were invalidated invalidated forfor this this period period because because of of an an unacceptably unacceptably high high coefficient coefficient ofof variation variation among among element element readings readings (not (not applicable applicable for for 2004 2004 data). data). (8) (8) Extra TLOs, Extra TLOs, notnot required required by TRMJOOCM (i.e. by TRMJOOCM (i.e. do do not not provide provide additional additional benefit) benefit) and and were were deleted deleted from from the the monitoring monitoring program. program. 1-7 1-7
("
.~. ,
('.. C,' :
.~
TABLE 1-2 TABLE 1-2 GROSS BETA, GROSS BETA, TRITIUM,AND TRITIUM,AND GAMMA GAMMA SPECTROSCOPIC SPECTROSCOPIC ANALYSES ANALYSES OF OF SURFACE SURFACE WATER WATER SUSQUEHANNA STEAM SUSQUEHANNA STEAM ELECTRIC ELECTRIC ST STAnON AnON -- 2004 2004 Results in Results pCilliter +/- in pCilliter 25
+/- 25 LOCATION LOCATION COLLECTION DATE COLLECTION DATE TRITIUM TRITIUM GR-BETA GR-BETA OTHER ACTIVITY OTHER ACTIVITY COMMENTS COMMENTS 6S6 6S6 12129/03 12129/03 01/26/04 01/26/04 136:1: 82 136:1: 82 <1.78
<1.78 2S7 2S7 12129103 12129103 01/26/04 01/26/04 405 :1:94 405 :1:94 9.3 2.2
- I: 2.2 9.3 :I:
6S5 6S5 12129103 12129103 01/26/04 01/26/04 <132
<132 2.6 ::I:
2.6 1.8
- I: 1.8 LTAW LTAW 01/12104 01/12104 243 :1:84 243 :1:84 3.8 :I:
3.8 1.4
- I: 1.4 6S6 6S6 01126/04 01126/04 03/01/04 03/01/04 <130
<130 <2.2
<2.2 K-40 K-40 46.2+/-26 46.2+/-26 2S7 2S7 01/26/04 01/26/04 03/01/04 03/01/04 12400 12400 :I: 243
- I: 243 11.9 2.7
- I: 2.7 11.9 :I: K-40 K-40 175+/-32 175+/-32 6S5 6S5 02102104 02102104 03/01104 03/01104 < 130
< 130 2.3 :I:
2.3 1.5
- I: 1.5 LTAW LTAW 02109/04 02109/04 187 ::1:86 187 ::1:86 3.4 ::t:
3.4 1.6
- t: 1.6 6S6 6S6 03/01/04 03/01/04 03/29/04 03/29/04 <126
<126 2.8 2.8 ::t: 1.1
- t: 1.1 2S7' 2S7' 03/01/04 03/01/04 03/29/04 03/29/04 9730 :1:225 9730 :1:225 8.5 :!:
8.5 :!: 1.8' 1.8' 6S5 6S5 03/08/04
' 03/08/04 03/29/04 03/29/04 < 134
< 134 4.4 :I:
4.4 1.3
- I: 1.3 LTAW LTAW 02109104 02109104 329 :1:94 329 :1:94 3.2 :!:
3.2 1.5
- !: 1.5 6S6 6S6 03/29/04 03/29/04 04127/04 04127/04 <126
<126 2.5 2.5 :I:
- I: 1.2 1.2 2S7 2S7 03/29/04 03/29/04 04/27/04 04/27/04 18400:1:287 18400:1:287 6.6 6.6 :I:
- I: 1.7 1.7 6S5 6S5 04/06/04 04/06/04 04/27/04 04/27/04 205:1:84 205:1:84 4.6 4.6 :!:
- !: 1.4 1.4 LTAW LTAW 04112104 04112104 169:1:85
169:1:85 2.8 2.8 :I:
- I: 1.4 1.4 6S6 6S6 04/27104 04/27104 06/01/04 06/01/04 <132
<132 <2.3
<2.3 2S7 2S7 04/27/04 04/27/04 06/01/04' 06/01/04' 390 :1:94 390 :1:94 7.8 7.8 2.5
- I: 2.5
- I:
6S5 6S5 05/04/04 05/04/04 06/01/04 06/01/04 <133
<133 <2.3
<2.3 LTAW LTAW 05110104 05110104 161 ::t:
161 132
- t: 132 3.7 :I:
3.7 1.9
- I: 1.9 6S6 6S6 06/01/04 06/01/04 06/29/04 06/29/04 <128
<128 2.3 2.3 :I:
- I: 1.4 1.4 2S7 2S7 06/01104 06/01104 06/29/04 06/29/04 3090 3090 :I: 141
- I: 141 11.1 11.1 :I:
- I: 2.6 2.6 6S5 6S5 06/08/04 06/08/04 06/29/04 06/29/04 <126
<126 <2.1
<2.1 LTAW LTAW 06114104 06114104 <134
<134 2.3 :!:
2.3 1.5
- !: 1.5 1-8 1-8
TABLE 1-2 TABLE 1-2 GROSS BETA, GROSS BETA, TRITIUM, TRITIUM, AND AND GAMMA GAMMA SPECTROSCOPIC SPECTROSCOPIC ANALYSES ANALYSES OF OF SURFACE SURFACE WATER WATER SUSQUEHANNA STEAM SUSQUEHANNA STEAM ELECfRIC ELECfRIC STATION STATION -- 2004 2004 Results in Results in pCUliter +/- 2S pCUliter +/- 2S LOCATION LOCATION COLLECTION DATE COLLECTION DATE TRITIUM TRITIUM GR-BETA GR-BETA OTHER ACTIVITY OTHER ACTIVITY COMMENTS COMMENTS 656 656 06129/04 06129/04 07/27/04 07/27/04 <127
<127 5.1 +/-
5.1 1.6
+/- 1.6 257 257 06129104 06129104 07/27/04 07/27/04 260 +/-85 260 +/-85 15.9 15.9 +/- +/- 3.0 3.0 655 655 07/061.04 07/061.04 07/27/04 07/27/04 <127
<127 4.2 +/-
4.2 +/- 1.5 1.5 LTAW LTAW 07/12104 07/12104 <121
<121 <2.1
<2.1 656 656 07/27/04 07/27/04 08/24/04 08/24/04 <135
<135 3.7 +/-
3.7 1.5
+/- 1.5 657 657 07/27/04 07/27/04 08/24/04 08/24/04 3870 3870 +/-+/- 158 158 13.5 13.5 +/- +/- 2.7 2.7 655 655 08103/04 08103/04 08/24/04 08/24/04 <134
<134 <2.0
<2.0 LTAW LTAW 08/09/04 08/09/04 261 +/-84 261 +/-84 3.7 +/-
3.7 +/- 1.7 1.7 656 656 08/24/04 08/24/04 09/28104 09/28104 244 +/-83 244 +/-83 7.4 % 7.4 1.7
% 1.7 257 257 08/24/04 08/24/04 09/28/04 09/28/04 3850 3850 +/-+/- 154 154 14.5 +/-
14.5 2.6
+/- 2.6 655 655 08/29/04 08/29/04 09/28/04 09/28/04 167 +/-80 167 +/-80 5.4 +/-
5.4 +/- 1.6 1.6
*LTAW 09/13/04 09/13/04 174 174 5.9 +/-
5.9 +/- 1.7 1.7 6S6 6S6 09/28/04 09/28/04 11/02104 11/02104 <132
<132 1.9 %
1.9 1.2
% 1.2 257 257 09/28/04 09/28/04 11/02104 11/02104 322 +/-89 322 +/-89 11.7 +/-
11.7 2.4
+/- 2.4 655 655 10/05104 10/05104 11/02104 11/02104 <132
<132 2.3 %
2.3 % 1.3 1.3 LTAW LTAW 10111/04 10111/04 <143
<143 2.4 +/-
2.4 +/- 1.3 1.3 656 656 11/02104 11/02104 11/30/04 11/30/04 156 % 156 79
% 79 2.8 +/-
2.8 1.5
+/- 1.5 257 257 11/02104 11/02104 11/30/04 11/30/04 312+/-
312+/- 8585 13.0 13.0 +/- +/- 2.7 2.7 655 655 11/02104 11/02104 11/30/04 11/30/04 186 +/- 186 +/- 79 79 3.5 % 3.5 1.5
% 1.5 LTAW LTAW 11115104 11115104 192+/-88 192+/-88 2.7 %
2.7 1.7
% 1.7 656 656 12107/04 12107/04 12128104 12128104 <133
<133 <2.0
<2.0 257 257 11/30/04 11/30/04 12128104 12128104 518+/- 101 518+/- 101 8.2 8.2 % 2.2
% 2.2 655 655 12107104 12107104 12128/04 12128/04 <135
<135 2.9 +/-
2.9 +/- 1.4 1.4 LTAW LTAW 12106/04 12106/04 <130
<130 .. <1.7
<1.7 1-9 1-9 c.
( .. co ( TABLE 1*3 TABLE IODINE-131 ANALYSES OF IODINE-131 ANALYSES OF SURFACE SURFACE WATER WATER SUSQUEHANNA STEAM SUSQUEHANNA STEAM ELECfRIC ELECfRIC STATION STATION -- 2004 2004 Results in pCilliter +/- 2S LOCATION COLLECTION DATE 1-131 COMMENTS 6S6 01/05/04 - 01119104 <0.40 2S7 01105/04 - 01/19/04 .76 +/-.45 SS5 01112104 - 01/19/04 .68+/- .34 SS6 02102104
- 02116/04 <.90 2S7 02102104
- 02116/04 <.93 6S5 02109/04
- 02116/04 <.90 6SS 03/01/04*03/15/04 <.73 2S7 03/01/04 - 03/15/04 <.73 SS5 03/08/04
- 03115/04 <.96 6S6 04/06/04
- 04120104 1.6 +/-1.8 "Refer to Appendix A for exceptions 2S7 04/06/04
- 04/20/04 . 1.6 +/- 2.1 *Refer to Appendix A for exceptions 6S5 04/13/04
- 04/20/04 1.1 +/- 1.6 *Refer to Appendix A for exceptions 6S6 05/04/04 - 05/18/04 .S3+/-.44 2S7 05/04/04 - 05/18/04 .93 +/-.67 6S5 05111104 - 05/18/04 <.63 6S6 06/08/04 ~ 06/22104 <.82 2S7 06/08/04
- 06/22/04 1.39 +/- .79 6S5 06/15/04 - 06/22/04 1.0+/- .49 6S6 07/06/04 - 07/20/04 <.90 6S7 07/06/04
- 07/20/04 1.0 +/- .75 6S5 . 07/13/04
- 07/20/04 <.79 1-10
TABLE 1*3 TABLE IODINE-131 IODINE-131 ANALYSES ANALYSES OF OF SURFACE SURFACE WATER WATER SUSQUEHANNA STEAM SUSQUEHANNA STEAM ELECfRIC ELECfRIC STATION STATION -- 2004 2004 Results in Results in pCilliter +/- 2S pCilliter +/- 2S LOCATION LOCATION COLLECTION DATE COLLECTION DATE 1*131 COMMENTS COMMENTS 6S6 08/03/04
- 08/17/04 <.59 6S7 08/03104 - 08117/04 1.32 %.84 6S5 08110/04*08117/04 <.55 6S6 09/07/04*09/21104 <.70 2S7 09/07/04*09/21104 <.82 6S5 09114/04 - 09/21/04 <.57 6S6 10/05/04
- 10119/04 <.68 2S7 10/05/04
- 10/19/04 1.29% .77 6S5 10/12104
- 10119/04 <.49 6S6 11102104 - 11/16/04 <.99 2S7 11/02104*11116104 <.88 6S5 11/09/04
- 11/16/04 <.92 6S6 12107104 -12121/04 <.72 6S7 12107104 -12121/04 <.79 6S5 12114104 - 12121/04 <.63 1*11
(
TABLE 1.4 TABLE 1.4 GROSS ALPHA, GROSS ALPHA, GROSS GROSS BETA, BETA, TRITIUM, TRITIUM, IODINE-131 GAMMA
- IODINE-131 GAMMA
- SPECTROSCOPIC SPECTROSCOPIC ANALYSES ANALYSES OF OF DRINKING DRINKING WATER WATER SUSQUEHANNA STEAM SUSQUEHANNA STEAM ELECTRIC ELECTRIC STATION* 2004 2004 Results Results in in pCilliter 2S
+/- 2S pCilliter +/-
LOCATION COLLECTION DATE GR*ALPHA GR*BETA TRITIUM OTHER ACTIVITY COMMENTS 12H2 12129/03*01/26/04 <1.76 <1.94 <133 12H2 01/26/04 - 03/01/04 <1.78 <2.21 <130 12H2 03/01 /04 - 03/29/04 <1.76 <1.83 <128 12H2 03129/04
- 04/26/04 <0.68 <1.74 <127 12H2 04/26/04*06/01/04 <1.21 <1.89 <126 12H2 06/01/04 - 06/29/04 <1.66 2.27 +/- 1.3 <120 12H2 06/29/04* 07/27/04 <1.42 <2.27 <124 12H2 07/27/04 - 08/24/04 <1.62 2.20+/- 1.3 <126 12H2 08/24/04
- 09/28/04 <1.53 3.09+/- 1.3 167 +/-78 12H2 09/28/04
- 11/02104 <1.55 1.95:1: 1.0 <131 12H2 11/02104
- 11/30/04 <1.45 2.65+/-1.34 195 +/-80 12H2 11/30/04
- 12128/04 <1.71 2.15:1: 1.3 168 +/-79 1*12
TABLE 1-5 GAMMA SPECTROSCOPIC ANALYSES OF FISH SUSQUEHANNA STEAM ELECTRIC STATION - 2004 Results in pCi/gm (wet) +/- 2S
c:' C" (" TABLE 1*6 TABLE GAMMA* GAMMA
- SPECTROSCOPIC SPECTROSCOPIC ANALYSES ANALYSES OF OF SHORELINE SHORELINE SEDIMENT SEDIMENT SUSQUEHANNA STEAM SUSQUEHANNA STEAM ELECTRIC ELECTRIC STATION STATION -- 2004 2004 Results in Results in pCi/gm pCi/gm (dry) +/- 2S (dry) +/- 2S LOCATION LOCATION COLLECTION DATE COLLECTION DATE K-40 K-40 Cs-137 Cs-137 Ra-226 Ra-226 TH-228 TH-228 OTHER ACTIVITY OTHER ACTIVITY 28 28 5/24/2004 5/24/2004 16.0:1: 2.3 16.0:1: 2.3 <.11
<.11 3.76 :1:2.5 3.76 :1:2.5 4.92:1: 2.0 4.92:1: 2.0 AC-228 AC-228 1.13:1: .46 1.13:1: .46 78 78 5/24/2004 5/24/2004 13.2:1: 2.1 13.2:1: 2.1 <.09
<.09 <1.37
<1.37 <1.26
<1.26 AC-228 AC-228 1.08:1: .39 1.08:1: .39 12F 12F 5/24/2004 5/24/2004 10.6:1: .1.6 10.6:1: .1.6 <.10
<.10 <2.0
<2.0 2.67:1: 1.6 2.67:1: 1.6 AC-228 AC-228 1.22:1: .39 1.22:1: .39 LTAW LTAW 5/24/2004 5/24/2004 14.9:1: 1.9 14.9:1: 1.9 <.08
<.08 <2.1
<2.1 3.61:1: 1.S 3.61:1: 1.S AC-228 AC-228 1.23 :1:.38 1.23 :1:.38 28 28 10/11/2004 10/11/2004 13.6:1: 1.1 13.6:1: 1.1 <.OS
<.OS 1.99:1: .86 1.99:1: .86 <.S1
<.S1 AC-228 AC-228 1.2S:I: .23 1.2S:I: .23 78 78 10111/2004 10111/2004 1S.4:1: 1.2 1S.4:1: 1.2 .10:1: .05
.10:1: .05 2.60:1: 1.2 2.60:1: 1.2 <1.01
<1.01 AC-228 AC-228 1.16:1: 0.3 1.16:1: 0.3 12F 12F 10/11/2004 10/11/2004 9.39 :1:.92 9.39 :1:.92 <O.OS
<O.OS 2.36:1: 1.1 2.36:1: 1.1 3.17:1: 1.1 3.17:1: 1.1 AC-228 AC-228 1.01 :I:
1.01 :I: .19
.19 LTAW LTAW 10/11/2004 10/11/2004 1S.3:1: 1.2 1S.3:1: 1.2 <.OS
<.OS 2.17:1: 1.1 2.17:1: 1.1 3.15:1: 1.1 3.15:1: 1.1 AC-228 AC-228 1.21 :I:
1.21 :I: .24
.24 1-14 1-14
C" (~. c' TABLE TABLE I*' AND GAMMA'" TRITIUM AND TRITIUM GAMMA'" SPECTROSCOPIC SPECTROSCOPIC ANALYSES ANALYSES OF OF GROUND GROUND WATER WATER SUSQUEHANNA STEAM SUSQUEHANNA STEAM ELECTRIC ELECTRIC STATION* 2004 2004 Results in Results in pCiI1iter +/- 2S pCiI1iter +/- 2S LOCATION LOCATION COLLECTION DATE COLLECTION DATE TRITIUM TRITIUM OTHER ACTIVITY OTHER ACTIVITY
'12F3
'12F3 111212004 111212004 <123
<123 252 252 1/1212004 1/1212004 <124
<124 454 Treated 454 Treated 111212004 111212004 <124
<124 12F3 12F3 219/2004 219/2004 <133
<133 252 252 219/2004 219/2004 <134
<134 454 Treated 454 Treated 219/2004 219/2004 <133
<133 12F3 12F3 3/15/2004 3/15/2004 128 +/-72 128 +/-72 252 252 3/15/2004 3/15/2004 <120
<120
.. 454 454 Treated Treated 3/15/2004 3/15/2004 <120
<120 12F3 12F3 4/1212004 4/1212004 <125
<125 252 252 r 411212004, 411212004, <126
<126 454 Treated 454 Treated 4/1212004 4/1212004 <123
<123 12F3 12F3 5110/2004 5110/2004 <132
<132 252 252 5/10/2004 5/10/2004 <132
<132 454 Treated 454 Treated 511012004 511012004 <121
<121 12F3 12F3 6/14/2004 6/14/2004 <119
<119 252 252 6/14/2004 6/14/2004 <131
<131 454 Treated 454 Treated 6/14/2004 6/14/2004 <132
<132 12F3 12F3 7/1212004 7/1212004 <123
<123 252 252 7/1212004 7/1212004 <124
<124 454 Treated 454 Treated 711212004 711212004 <124
<124 12F3 12F3 8/9/2004 8/9/2004 <124
<124 252 252 8/9/2004 8/9/2004 <123
<123 454 Treated 454 Treated 8/9/2004 8/9/2004 <121
<121 1-15 1-15
TABLE I*' TABLE TRITIUM AND TRITIUM GAMMA* AND GAMMA
- SPECTROSCOPIC SPECTROSCOPIC ANALYSES ANALYSES OF OF GROUND GROUND WATER WATER SUSQUEHANNA STEAM ELECTRIC SUSQUEHANNA STEAM ELECTRIC STATION STATION -- 2004 2004 Results in pCilliter +/- 2S LOCATION COLLECTION DATE TRITIUM OTHER ACTIVITY 12F3 9/1312004 <126 2S2 9/1312004 <126 4S4 Treated 9113/2004 <131 12F3 10/11/2004 <133 2S2 10/11/2004 <133 4S4 Treated 10/11/2004 <132 12F3 11/15/2004 <133 2S2 11/15/2004 <134 4S4 Treated 11/15/2004 <134 12F3 1211312004 <129 2S2 12113/2004 <124 4S4 Treated 1211312004 <104*
*H*3 Sample rerun result 1*16
( (~..
( GROSS BETA GROSS BETA ANALYSFS ANALYSFS OF T{ T{ ~1*8 OF AIR AIR PARTICULATE PARTICULATE FILTERS FILTERS c SUSQUEHANNA SUSQUEHANNA STEAM STEAM ELECTRIC ELECTRIC STATION* 2004 2004 Results in Results in E-03 E-03 pCilCu. pCilCu. M. M. +/-+/-2S 2S COLLECTION COLLECTION MONTH,' MONTH,' DATE DATE , I 6G1, : 6G1, ',8G1
',8G1 352 352 12E1 12E1 12S1: ,,
12S1: ,, 13S6 13S6 COMMENTS COMMENTS JAN JAN 12130/03 -1fl 12130/03 -1fl 04 04 13.7 13.7 +/-
+/- 2.12.1 22.9 £2.5, 22.9 £2.5, 17.0 £2.3 17.0 £2.3 17.2 17.2 +/-2.2
+/-2.2 17.6 17.6 +/-
+/- 2.22.2 16.7,+/-
16.7,+/- 2.2 2.2 1flI04-.1114/04 1flI04-.1114/04 16.8 16.8 +/- 2.5
+/- 2.5 15.3' +/-'
15.3' +/-' 2.3' 2.3' 18.8;+/-'2.6 18.8;+/-'2.6 18.3', 18.3', +/- 2.0
+/- 2.0 20.3 20.3 2.5'
+/- 2.5'
+/- 19.8 :t: 2.6 19.8 :t: 2.6 1114/04 -1/21/04 1114/04 -1/21/04 6.97 6.97 +/- 1.8
+/- 1.8 6.4 +/-
6.4 +/- 1.6 1.6 9.2 +/- 9.2 +/- 1.9 1.9 9.4 9.4 1.8
+/- 1.8
+/- 9.4 9.4 1.9
+/- 1.9
+/- 8.6 +/-
8.6 1.9
+/- 1.9 1121104 -1/28/04 1121104 -1/28/04 14.1 14.1 +/- 2.2
+/- 2.2 10.0 +/-
10.0 +/- 2~1 13.4 £2Ji 13.4 £2Ji 14.T 14.T +/-'2.4
+/-'2.4 14.5 14.5 2:3
+/- 2:3
+/- 11.9 +/-
11.9 +/- 2.0 2.0 FEB FEB 1/28104 -- 214/04, 1/28104 214/04, 11;4 11;4 +/- 2.3
+/- 2.3 14.2 14.2 +/- 2.3
+/- 2.3 15.4 15.4 +/- 2.3
+/- 2.3 12.8 12.8 +/- 2.2,
+/- 2.2, .. 13.6, 13.6, +/- +/- 2.3 2.3 12.2 12.2 +/- 2.1
+/- 2.1 214/04,- 2111/04-- 13.5 214/04,- 2111/04-- 13.5 +/-
+/- 2.32.3 11.9 11.9 +/- 2.2
+/- 2.2 15.4 15.4 +/- 2.3
+/- 2.3 15.1' 15.1' +/- 2.4
+/- 2.4 15.7 +/-
15.7 +/- 2.5 2.5 14.4 14.4 +/- 2.3
+/- 2.3 2111/04. -- 2118/04 2111/04. 2118/04 .. 20.1 20.1 +/-
+/- 2.6 2.6 21.2 21.2 +/- 2.7
+/- 2.7 20.5 20.5 +/- 2.8
+/- 2.8 21.6 21.6 +/- 2.7
+/- 2.7 19.0 +/-
19.0 +/- 2.6 2.6 19.2 19.2 +/- 2.7
+/- 2.7 2118/04 -- 2125/04 2118/04 2125/04 21 21 +/- 2.6
+/- 2.6 ,, 15.7 15.7 +/- 2.4
+/- 2.4 24.2 24.2 +/- 2.9
+/- 2.9 22.2 22.2 +/- 2.7
+/- 2.7 21.3 +/-
21.3 +/- 2.7 2.7 19.9 19.9 +/- 2.7
+/- 2.7
'~~::\,-, ~ . . ~.
MAR 2125/04 MAR 2125/04 -- 3/3/04 3/3/04 14.9 14.9 +/- 2.3
+/- 2.3 15.3 15.3 +/- +/- 2.4 2.4 17.7, 2.5 17.7, +/-+/- 2.5 17.1, 17.1, +/- 2.4
+/- 2.4 14.4 14.4 +/- 2.3
+/- 2.3 14.9 14.9 +/- 2.4,
+/- 2.4, 3/3/04 .;.; 3/10/04.',
3/3/04 3/10/04.', 9.7~ +/-
+/- 1.9 1.9 9.4* +/-+/- 1~9 12.2 +/-
12.2 +/- 2.2 2.2 12.4 12.4 +/- 2.1:
+/- 2.1: 12.6 12.6 +/- 2.1:
+/- 2.1: 11.2 11.2 +/- 2.1
+/- 2.1 3/10/04 -- 3117/04 3/10/04 3117/04 9.5'....
9.5' +/- 2.1;
+/- 2.1; 10.6 :1:'2.2 10.6 :1:'2.2 £2.4 12.9 £2.4 12.9 10.8 10.8 +/- 2.2
+/- 2.2 11.8 11.8 +/- 2.2
+/- 2.2 9:6 9:6 +/- 2.2
+/- 2.2 3/17/04 -- 3/24/04 3/17/04 3/24/04 12.6 12.6 :I: 2.1
- I: 2.1 11.6 +/-+/- 2.1 11.6 2.1 10.5 +/-
10.5 +/- 2.1 2.1 12.0 12.0 +/- 2.2
+/- 2.2 13.9 13.9 +/- 2.2
+/- 2.2 12.8 12.8 2.3
+/- 2.3
+/-
3/24/04- 3/31/04' 3/24/04- 3/31/04' 11~8 2.2
- I: 2.2
- I: 13.2 +/-
13.2 +/- 2.3 2.3 12.7, :1:'2.3 12.7, :1:'2.3 14.4' 14.4' 2.4
+/- 2.4
+/- 12.5 12.5 £2.2
£2.2 15.7 15.7 2.5
+/- 2.5
+/-
"" JJ -- :-'
- -' JJ APR APR 3/31/04 -:4flI04 3/31/04 -:4flI04 5.7 +/-
5.7 +/- 2.0 2.0 4;4', +/- 4;4', 2:0
+/- 2:0 4.4:
4.4: +/- 2.0
+/- 2.0 6.5 6.5 +/- 2.2
+/- 2.2 3.5 3.5 :t: 22
- t: 3.9 3.9 :t: 2.1
- t: 2.1 4fl 104 -- 4114104 4fl104 4114104 10.7 10.7 :I: :I: 2.02.0 11~8 +/-'2.0
+/-'2.0 12.2 12.2 +/- 2.1'
+/- 2.1' 14.8 14.8 2.3
+/- 2.3
+/- 11.5 11.5 :t: 2.0
- t: 2.0 11.0 11.0 +/- 2.1
+/- 2.1 4/14/04 -- 4/21104 4/14/04 4/21104 14.5 +/-
14.5 +/- 2.4 2.4 16.1 +/- 16.1 +/- 2.5 2.5 16.4 16.4 +/- 2.6
+/- 2.6 15.2 15.2 +/- 2.5
+/- 2.5 15.5 15.5 :t: 2.5
- t: 2.5 14.2 14.2 +/- 2.3
+/- 2.3 4/21/04 -- 4/28/04 4/21/04 4/28/04 8.2 +/-
8.2 +/- 2.0 2.0 8.0 +/- 8.0 +/- 2.0 2.0 9.8 9.8 2.2
+/- 2.2
+/- 10.8 10.8 +/- 2.1
+/- 2.1 10.0 10.0 +/- 2.2
+/- 2.2 9.9 9.9 +/- 2.1
+/- 2.1 MAY 4/28/04 MAY 4/28/04 -- 5/05/04 5/05/04 11~4 +/- +/- 2.1 2.1 12.7 12.7 +/- 2.2
+/- 2.2 13.9 13.9 +/- 2.3
+/- 2.3 11.2 11.2 +/- 2.1
+/- 2.1 12.9 12.9 +/- 2.2
+/- 2.2 12.3 12.3 +/- 2.0
+/- 2.0 5/5104 -- 5/12104 5/5104 5/12104 18.2 +/-
18.2 +/- 2.6 2.6 19.5 19.5 +/- 2.7
+/- 2.7 17.2 17.2 +/- 2.7
+/- 2.7 17.8 17.8 +/- 2.7
+/- 2.7 17.1 17.1 +/-
+/- 2.52.5 18.6 18.6 +/- 2.7
+/- 2.7 5112104 -- 5/19/04 5112104 5/19/04 15.0 +/-
15.0 +/- 2.5 2.5 13.4 13.4 +/- 2.4
+/- 2.4 17.8 17.8 2,6
+/- 2,6
+/- 13.9 13.9 +/- 2.2
+/- 2.2 17.1 17.1 :t:2.6
- t:2.6 15.8 15.8 +/- 2.5
+/- 2.5 5/19/04 -- 5/26/04 5/19/04 5/26/04 15.7 +/-+/- 2.6 15.7 2.6 13.3 13.3 +/- 2.5
+/- 2.5 15.0 15.0 +/-'2.4
+/-'2.4 12.7 12.7 +/- 2.2
+/- 2.2 13.2 13.2 :t: 2.4
- t: 2.4 13.0 13.0 :t: 2.4
- t: 2.4 II .....
..... ,, t t
JUN JUN 05/26/04.; 05/26/04.; 612104 612104 9.2 9.2 +/-
+/- 2.0 2.0 13.0 13.0 +/- 2.3
+/- 2.3 10.5 10.5 +/- 2.0
+/- 2.0 9.8 9.8 +/-
+/- 1.9 1.9 9.7 9.7 ii :t: 2.0
- t: 2.0 9.2 9.2 +/- +/- 2.0 2.0 6/2104 -- 6/9/04:
6/2104 6/9/04: 11.0 11.0 +/- 2.3
+/- 2.3 10.7 10.7 +/- 2.3
+/- 2.3 11.1 11.1 +/- 2.2
+/- 2.2 12.0 12.0 +/- 2.1
+/- 2.1 12.4 12.4 :t: 2.3
- t: 2.3 9.7 +/-+/- 2.1 9.7 2.1 619/04,- 6116/04 619/04,- 6116/04 12.4 12.4 +/- 2.2
+/- 2.2 11.5 11.5 +/- 2.1
+/- 2.1 11.9 11.9 +/- 2.1
+/- 2.1 10.9 10.9 +/- 1.9
+/- 1.9 11.8 11.8 +/- 2.1
+/- 2.1 14.3 +/-
14.3 +/- 2.3 2.3 6/16/04 -- 6/23/04 6/16/04 6/23/04 9.8 9.8 +/- 2.1
+/- 2.1 10.7 10.7 +/- 2.2
+/- 2.2 10.7 10.7 +/- 2.1
+/- 2.1 11.7 11.7 2.1
+/- 2.1
+/- 8.5 8.5 +/- 2.1
+/- 2.1 10.7 +/-
10.7 +/- 2.2 2.2 6/23/04 -- 6/30/04 6/23/04 6/30/04 13.0 13.0 +/- 2.4
+/- 2.4 12.5 12.5 +/- 2.3
+/- 2.3 12.1 12.1 +/- 2.2
+/- 2.2 13.2 13.2 ,+/- 2.2
,+/- 2.2 12.7 12.7 +/- 2.4
+/- 2.4 14.7. +/-+/- 2.4 14.7. 2.4
.. ;; JJ ~;
1*11
TABLE 1-8 TABLE 1-8 GROSS BETA ANALYSES GROSS BETA ANALYSES OF OF AIRAIR PARTICULATE PARTICULATE FILTERS FILTERS SUSQUEHANNA STEAM SUSQUEHANNA STEAM ELECfRIC ELECfRIC STATION STATION -- 2004 2004 Results in Results E-03 pCilCu. in E-03 pCilCu. M. M. +/-+/- 2S2S COLLECTION COLLECTION MONTH MONTH DATEDATE 6G1 6G1 8G1 8G1 3S2 3S2 12El 12El 12Sl 12Sl l3S6 l3S6 COMMENTS COMMENTS JUL JUL 6/30/04 7n 6/30/04 ** 7 n104 104 16.2 16.2 +/-
+/- 2.5 2.5 15.1 15.1 +/- 2.5
+/- 2.5 16.4 16.4 +/- 2.5
+/- 2.5 16.5 16.5 +/- 2.4
+/- 2.4 16.1 :t 2.6 16.1 :t 2.6 13.6 :t 2.4 13.6 :t 2.4 7fll04 -- 7114/04 7fll04 7114/04 6.0 6.0 +/-
+/- 1.9 1.9 8.3 8.3 +/-
+/- 2.0 2.0 7.1 7.1 +/-
+/- 2.0 2.0 8.0 8.0 +/- 2.0
+/- 2.0 7.6 :t 7.6 :t 2.0 2.0 7.6 :t 7.6 :t 2.0 2.0 7/14/04 -- 7/21/04 7/14/04 7/21/04 12.8 12.8 +/-
+/- 2.3 2.3 12.9 12.9 +/-
+/- 2.3 2.3 12.2 12.2 +/-
+/- 2.2 2.2 12.0 12.0 +/-
+/- 2.1 2.1 13.0 :t 13.0 :t 2.3 2.3 11.4 +/-+/- 2.2 11.4 2.2 7/21/04 -- 7/28/04 7/21/04 7/28/04 12.4 12.4 +/-
+/- 2.3 2.3 13.9 13.9 +/- 2.3
+/- 2.3 14.0 14.0 +/-
+/- 2.2 2.2 15.1 15.1 +/- 2.3
+/- 2.3 13.5 +/-
13.5 +/- 2.3 2.3 17.1 +/- 17.1 +/- 2.5 2.5 AUG AUG 7/28/04 -- 8/4104 7/28/04 8/4104 14.5 14.5 +/- 2.3
+/- 2.3 12.3 12.3 :t
- t 2.1 2.1 13.3 13.3 :t
- t 2.1 2.1 14.5 14.5 :t
- t 2.2 2.2 12.4 :t 12.4 :t 2.1 2.1 16.3 16.3 +/-
+/- 2.4 2.4 8/4/04 -- 8/11104 8/4/04 8/11104 14.0 14.0 :t 2.3
- t 2.3 14.4 14.4 +/- 2.3
+/- 2.3 13.9 13.9 +/-
+/- 2.2 2.2 36.6 36.6 +/- 3.2
+/- 3.2 12.3 :t 12.3 :t 2.2 2.2 12.8 12.8 +/- 2.3
+/- 2.3 8/11/04 -- 8/18/04 8/11/04 8/18/04 13.7 13.7 +/- 2.2
+/- 2.2 15.0 15.0 :t 2.3
- t 2.3 13.1 13.1 +/- 2.1
+/- 2.1 14.7 14.7 2.2
+/- 2.2
+/- 15.6 ::I::
15.6 2.3
- I:: 2.3 14.0 14.0 +/-
+/- 2.3 2.3 8/18/04 -- 8125104 8/18/04 8125104 18.1 18.1 +/- 2.7
+/- 2.7 19.2 19.2 +/- 2.6
+/- 2.6 18.3 18.3 +/- 2.5
+/- 2.5 13.7 13.7 2.3
+/- 2.3
+/- 18.9 +/-+/- 2.7 18.9 2.7 19.4 19.4 +/-
+/- 2.8 2.8 8/25/04 -- 9/1104, 8/25/04 9/1104, 13,1 13,1 +/- 2.3
+/- 2.3 12.2 12.2 :t 2.2
- t 2.2 14.0 14.0 +/-
+/- 2.2 2.2 13.8 13.8 :t 2.2
- t 2.2 15.5 ::I::
15.5 2.4
- I:: 2.4 14.2 14.2 +/- 2.4
+/- 2.4 SEP SEP 9/1104 -- 9/8/04 9/1104 9/8/04 12.3 12.3 +/-
+/- 2.3 2.3 13.7 13.7 +/- 2.4
+/- 2.4 13.5 13.5 +/- 2.2
+/- 2.2 14.0 14.0 +/- 2.3
+/- 2.3 12.3 ::I::
12.3 2.2
- I:: 2.2 15.4 15.4 +/- 2.6
+/- 2.6 9/8104 -- 9115/04 9/8104 9115/04 10.6 10.6 +/-
+/- ### ### 11.2 11.2 :t 2.1
- t 2.1 10.1 10.1 :t
- t 2.02.0 9.4 9.4 :t 1.9
- t 1.9 10.7 :t2.1 10.7 :t2.1 9.7 9.7 +/- 2.1
+/- 2.1 9/15/04 -- 9/22104 9/15/04 9/22104 9.9 9.9 +/- 2.1
+/- 2.1 9.6 9.6 +/- 2.0
+/- 2.0 9.9 9.9 +/- 2.1
+/- 2.1 9.8 9.8 +/-2.0
+/-2.0 11.9 +/-
11.9 +/- 2.1 2.1 11.6 11.6 +/-
+/- 2.4 2.4 9/22104 -- 9/29/04 9/22104 9/29/04 20.9 20.9 +/- 2.7
+/- 2.7 18.0 18.0 :t 2.4
- t 2.4 23.0 23.0 +/- 2.9
+/- 2.9 22.2 22.2 +/- 2.6
+/- 2.6 22.2 :t 22.2 :t 2.6 2.6 20.4 20.4 +/- 2.6
+/- 2.6 OCT OCT 10/6/04 9/29/04 -- 10/6/04 9/29/04 14.0 :t 14.0 :t 2.2 2.2 13.2 +/-
13.2 +/- 2.3 2.3 13.1 +/-+/- 2.3 13.1 2.3 15.2 :t 15.2 2.3
- t 2.3 12.6 :t 12.6 :t 2.1 2.1 13.1 ::I::
13.1 2.2
- I:: 2.2 11016104 016104 ~ 10/13104 10/13104 19.6 :t 2.6 19.6 :t 2.6 19.9 :t 19.9 :t 2.7 2.7 21.7 21.7 :t:t 2.82.8 18.9 18.9 :t 2.6
- t 2.6 18.1 :t 18.1 :t 2.4 2.4 22.4 :t 2.8 22.4 :t 2.8 10/13/04 -- 10/20/04 10/13/04 10/20/04 9.4 +/-
9.4 +/- 2.1 2.1 9.8 +/-+/- 2.1 9.8 2.1 10.4 :t 10.4 :t 2.22.2 10.7 +/-+/- 2.1 10.7 2.1 12.0 ::I:: 12.0 ::I:: 2.1 2.1 11.2 +/-+/- 2.3 11.2 2.3 10/20/04 -- 10/27/04 10/20/04 10/27/04 7.2 +/- 7.2 +/- 1.9 1.9 10.8 ::I:: 10.8 2.2
- I:: 2.2 8.2 :t 8.2 :t 2.02.0 10.0 +/-+/- 2.0 10.0 2.0 9.6 :t 9.6 :t 1.9 1.9 10.2 +/-+/- 2.2 10.2 2.2 NOV NOV 10/27/04 10/27/04 -11/03 04
-11/03 04 10.9 10.9 +/- 2.1
+/- 2.1 12.9 12.9 ::I:: 2.3
- I:: 2.3 14.1 14.1 ::I::
- I:: 2.5 2.5 14.7 14.7 :t 2.4
- t 2.4 15.0 15.0 ::I::
- I:: 2.6 2.6 13.2 13.2 +/-
+/- 2.3 2.3 11/3104 -- 11/10/04 11/3104 11/10/04 12.1 12.1 2.3
- I:: 2.3
- I:: 12.0 ::I::
12.0 2.3
- I:: 2.3 12.3 12.3 :t 2.3
- t 2.3 11.0 11.0 +/- 2.1
+/- 2.1 12.7 12.7 +/-
+/- 2.4 2.4 10.4 10.4 +/-
+/- 2.2 2.2 11110104 -11117/04 11110104 -11117/04 10.7 10.7 +/- 2.0
+/- 2.0 14.5 +/-+/- 2.3 14.5 2.3 16.7 16.7 +/- 2.4
+/- 2.4 14.5 14.5 +/- 2.3
+/- 2.3 16.9 16.9 :t 2.5
- t 2.5 17.2 17.2 +/-
+/- 2.4 2.4 11/17104 -11/24/04 11/17104 -11/24/04 16.8 16.8 +/- 2.5
+/- 2.5 17.2 +/-+/- 2.6 17.2 2.6 20.4 20.4 +/- 2.8
+/- 2.8 21.5 21.5 +/- 2.8
+/- 2.8 24.1 24.1 +/- 3.0
+/- 3.0 22.8 22.8 +/-
+/- 2.9 2.9 11/24104 -1211104 11/24104 -1211104 10.4 10.4 +/- 2.1
+/- 2.1 9.3 +/-+/- 2.1 9.3 2.1 8.6 8.6 +/- 2.1
+/- 2.1 10.2 10.2 2.1
+/- ,,2.1
+/- 8.1 8.1 +/- 2.1
+/- 2.1 9.0 9.0 +/-
+/- 2.1 2.1 DEC DEC 1211104 -- 1218104 1211104 1218104 14.1 +/-
14.1 +/- 2.2 2.2 14.8 14.8 +/-+/- 2.3 2.3 16.2 16.2 +/-+/- 2.4 2.4 16.6 16.6 :t'2.4
- t'2.4 15.0 :t 15.0 :t 2.42.4 15.9 15.9 :t:
- t: 2.4 2.4 1218/04 -- 12115/04 1218/04 12115/04 7.6 :t 7.6 :t 1.8 1.8 9.0 :t 9.0 :t 2.0 2.0 7.6 :t 7.6 :t 1.91.9 7.9 7.9 :t ll l.9
- t l.9 8.5 :t 8.5 :t 2.02.0 9.7 9.7 +/-
+/- 2.1 2.1 12115/04 -12121/04 12115/04 -12121/04 13.7 +/-
13.7 +/- 2.42.4 15.4 +/-+/- g.5 15.4 g.5 14.9 :t 14.9 :t 2.52.5 15.5 15.5 2.5
- t: 2.5
- t: 16.7 :t 16.7 :t 2.62.6 15.2 15.2 :t:
- t: 2.5 2.5 12121104 -12128104 12121104 -12128104 12.3 :t:
12.3 2.2
- t: 2.2 13.5 :t 13.5 :t 2.22.2 13.7 :t 13.7 :t 2.32.3 13.8 13.8 :t'2.3
- t'2.3 13.3 :t 13.3 :t 2.32.3 13.3 13.3 :t 2.3'
- t 2.3'
(*18 c (
C ThLEI.9 ThLEI.9 ( GAMMA'" SPECTROSCOPIC GAMMA'" SPECTROSCOPIC ANALYSES ANALYSES OF OF COMPOSITED COMPOSITED AIR AIR PARTICULATE PARTICULATE FILTERS FILTERS SUSQUEHANNA STEAM SUSQUEHANNA STEAM ELECfRIC ELECfRIC STATION STATION -- 2004 2004 Results in Results in E-03 E-03 pCi/Cu. pCi/Cu. M. +/- 2S M. +/- 2S LOCATION COLLECTION DATE Be-7 K*40 ACTIVITY OTHER ACTIVITY 6G1 12130/03
- 3/31/04 80.2:t9.25 <3.19 8G1 12130/03*3/31/04 73.6:t8.57 <2.36 382 12130/03
- 3/31/04 78.3 :t3.S <0.94 12E1 12130/03*3/31/04 89.4:t 11.1 <4.63 1281 12130103
- 3/31/04 77.4 :t4.79 <3.79 1386 12130103
- 3/31104 79.3:t3.40 <1.84 6G1 3/31/04*6/30/04 105:t 12.6 <6.62 8G1 3/31/04*6/30104 109:t 13.3 <6.68 382 3/31/04*6/30/04 132:t 16.2 <10.7 12E1 3/31/04*6/30/04 116:t 13.3 <8.96 12S1 3/31/04*6/30/04 120:t 18.5 <13.9 13S6 3/31/04*6/30/04 108+/- 17.4 <11.5 6G1 6/30/04 - 9/29/04 89.3 +/- 11.6 <9.32 8G1 6/30/04
- 9129104 91.5:t 10.8 <4.28 382 6/30/04
- 9129104 9S.3:t 10.9 <3.95 12E1 6/30/04
- 9/29/04 93.1 :t 11.6 <3.27 1281 6/30/04
- 9/29/04 99.7:t 10.2 <5.48 1386 6/30/04
- 9/29/04 56.8:t 11.1 <10.3 6G1 9/29/04 - 12128/04 78.5:t 14.3 <10.9 8G1 9/29/04 - 12128/04 75.5:t 11.6 <7.81 382 9/29/04
- 12128/04 74.8:t 16.1 <14.3 12E1 9/29/04 - 12128104 83.1 +/- 12.2 <2.79 12S1 9/29/04
- 12128/04 81.9:t 13.5 <10.5 13S6 9/29/04 - 12128/04 75.9 :t 12.0 <10.2 1*19
c ( TABLE TABLE 1*10 c IODINE-I3I, AND GAMMA'" IODINE-I3I, AND GAMMA'" SPECTROSCOPIC SPECTROSCOPIC ANALYSES ANALYSES OF OF MILK MILK SUSQUEHANNA STEAM SUSQUEHANNA STEAM ELECTRIC ELECTRIC STATION STATION -- 2004 2004 Results in Results in pCiniter +/- 2S pCiniter +/- 2S LOCATION LOCATION COLLECTION DATE COLLECTION DATE K-40 K-40 OTHER ACTIVITY OTHER ACTIVITY COMMENTS COMMENTS 10Gl 10Gl 01/05/04 01/05/04 1420 1420 +/- +/- 160 160 1001 1001 01/05/04 01/05/04 1320 +/- 1320 +/- 130 130 1002 1002 01/05/04 01/05/04 1350 +/- 1350 +/- 140 140 12B2 12B2 01105104 01105104 1420 +/- 1420 +/- 160 160 10Gl 10Gl 02103/04 02103/04 1460 1460 % %110 110 100'1 100'1 02103164 02103164 1350 % 1350 %130 130 1002 1002 02103/04 02103/04 1380 % 1380 %150 150 1282 1282 02103/04 02103/04 1440 % 1440 %110 110 10G1 10G1 03/08/04 03/08/04 1620;';150 1620;';150 1001 1001 '03108/04
'03108/04 1470:i: 150 1470:i: 150 1002 1002 '03/08/04
'03/08/04 1420"% '140 1420"% '140 1282 1282 '03iOB/04
'03iOB/04 1530 %
1530 %140 140 l'O"G1 l'O"G1 'o4i05/04
'o4i05/04 1480 1480 % % '110
'110 1001 1001 04/05104 04/05104 1440 %
1440 % 110 110 1002 1002 04/05/04 04/05/04 13'60 % 13'60 % 110 110 1282 1282 04/05/04 04/05/04 1440 % 1440 %160 160 10G"1 10G"1 04i1'9/04 04i1'9/04 1460 % 1460 % 140 140 1001 1001 '04119/04
'04119/04 1460 1460 +/- +/- 140 140 1002 1002 04/19/04 04/19/04 ff 440 440 %160.
%160.
1282 1282 04119104 04119104 1540% -140 1540% -140 10Gl 10Gl '05103/0'4
'05103/0'4 1440 %
1440 %110 110 100"1 100"1 '05/03/04
'05/03/04 1480 +/-:110 1480 +/-:110 1002 ..
1002 05103104 05103104 1250 +/-: 1250 +/-: 120 120 -. 1282" , 1282" 05/03/04' 05/03/04' 1500 +/-+/- 160 1500 160 10G1 10G1 05/19/04 05/19/04 1520 % 1520 %170 170
TABLE 1*10 TABLE IODINE-131, AND IODINE-131, GAMMA* AND GAMMA
- SPECTROSCOPIC SPECTROSCOPIC ANALYSES ANALYSES OF OF MILK MILK SUSQUEHANNA STEAM SUSQUEHANNA STEAM ELECfRlC ELECfRlC STATION* 2004 2004 Results in Results +/-2S in pCilliter +/- 2S LOCATION COLLECTION DATE K-4O OTHER ACTIVITY COMMENTS 1001 05119/04 1550 +/- 150 1002 05/19/04 1380 +/- 130 1282 05119104 1460 +/- 130 10Gl 06/03/04 1520 +/- 110 1001 06/03/04 1430 +/- 130 1002 06/03/04 1450 +/- 130 1282 06/03/04 1510 +/- 130 10Gl 06/20/04 1467 +/ 1001 06/20/04 1370 +/- 110 1002 06/20/04 1150+/- 120 *Refer to Appendix A for exceptions 1282 06/20/04 1430 +/- 130 10Gl 07/06/04 1350 +/- 150 1001 07/06/04 1520+/- 140 1002 07/06/04 1250 +/- 140 1282 07/06/04 1450 +/- 160 10G1 07119104 1430 +/- 190 1001 07119/04 1220 +/- 190 1002 07119/04 1410+/- 160 1282 07119/04 1350 +/-150
( ( (
c ( " TABLE 1*10 TABLE IODINE-131, AND GAMMA'" IODINE-131, AND GAMMA'" SPECTROSCOPIC SPECTROSCOPIC ANALYSESANALYSES OF OF MILK MILK SUSQUEHANNA STEAM SUSQUEHANNA STEAM ELECTRIC ELECTRIC STATION STATION -- 2004 2004 Results in Results in pCilliter +/- 2S pCilliter +/- 2S LOCATION OTHER ACTIVITY OTHER ACTIVITY COMMENTS COMMENTS 10G1 10G1 *Refer to
*Refer to Appendix Appendix A A for for exceptions exceptions 1001 1001 1002 1002 1282 1282 10G1 10G1 1001 1001 1002 1002 1282 1282 10G1 10G1 1001 1001 *Refer to Appendix
*Refer to Appendix A A for for exceptions exceptions 1002 1002 "Refer to "Refer to Appendix Appendix A A for for exceptions exceptions 1282 1282 10<31 10<31 1001 1001 1002 1002 1282 1282 10(3'1 1001 1001 1002 1002 1282 1282
"" 1*22
TABLE 1*10 TABLE AND GAMMA'" IODlNE*131, AND GAMMA'" SPECTROSCOPIC SPECTROSCOPIC ANALYSESANALYSES OF OF MILK MILK SUSQUEHANNA STEAM SUSQUEHANNA STEAM ELEcrRIC ELEcrRIC STATION STATION -- 2004 2004 Results in Results in pCUliter +/- 2S pCUliter +/- 2S LOCATION LOCATION COLLECTION DATE COLLECTION DATE K-40 K-40 OTHER ACTIVITY OTHER ACTIVITY COMMENTS COMMENTS 10Gl 10Gl 10/18104 10/18104 1370:t 110 1370:t 110 1001 1001 10/18104 10/18104 1460:t 130 1460:t 130 1002 1002 10/18104 10/18104 1310:t 150 1310:t 150 12B2 12B2 10/18/04 10/18/04 1210:t 120 1210:t 120 10Gl 10Gl 11/08/04 11/08/04 1580:t 160 1580:t 160 1001 1001 11/08/04 11/08/04 1420:t 160 1420:t 160 1002 1002 11/08104 11/08104 1370:t 160 1370:t 160 12B2 12B2 11108/04 11108/04 1360:t 150 1360:t 150 10Gl 10Gl 12106104 12106104 1460:t 130 1460:t 130 1001 1001 12106104 12106104 1570:t 140 1570:t 140 1002 1002 12106104 12106104 1360:t 130 1360:t 130 12B2 12B2 12106104 12106104 1300:t 120 1300:t 120 (( ,, (( (( 1-23 1-23 rr
cc (( TABLE TABLE 1.111.11 (( SPECTROSCOPIC ANALYSES GAMMA* SPECTROSCOPIC ANALYSES OF OF SOIL SOIL SUSQUEHANNA STEAM SUSQUEHANNA STEAM ELECTRIC ELECTRIC STATION STATION -- 2004 2004 Results in Results in pCifgm pCifgm (dry) +/- 25 (dry) +/- 25 LOCATION LOCATION COLLECTION DATE COLLECTION DATE K-40 K-40 Cs-137 Cs-137 Th-228 Th-228 8G1TOP 8G1TOP 9/15/2004 10.4 10.4 +/- +/- 1.3 1.3 0.14+/- .06 0.14+/- .06 0.77 +/- 0.77 +/- .15
.15 8G1BOT 8G1BOT 9115/2004 8.1 +/-
8.1 +/- .61
.61 0.078+/- .028 0.078+/- .028 0.B4+/-.08 3S2TOP 3S2TOP 9/15/2004 13.9 13.9 +/-+/- 1.1 1.1 0.07B+/- .041 0.98 +/- .12 0.98 +/- .12 3S2BOT 3S2BOT 9/15/2004 14.1 +/-
14.1 +/- 1.1 1.1 <.OB 1.01 +/- 1.01 +/- .12
.12 12S1 TOP 12S1 TOP 9/15/2004 12.4 +/-
12.4 +/- .95
.95 .. <.05
<.05 0.77 +/-
0.77 .11
+/- .11 12S1 BOT 12S1 BOT 911512004 12.0 +/-0.82 12.0 +/-0.82 <.04
<.04 0.88 +/- .09 0.88 +/- .09 13SBTOP 13SBTOP 9/15/2004 18.5 +/-
18.5 +/- 1.0 1.0 <.05
<.05 1.18 +/- .19 1.18 +/- .19 13SB BOT 13SB BOT 9/15/2004 1B.0+/-.03 <.06
<.06 <.23
<.23 1-24 1-24
(( (( (( TABLE 1*12 TABLE GAMMA* SPECTROSCOPIC GAMMA* SPECTROSCOPIC ANALYSES ANALYSES OFOF FOOD FOOD PRODUCTS PRODUCTS (FRUITS (FRUITS AND AND VEGETABLES) VEGETABLES) SUSQUEHANNA STEAM SUSQUEHANNA STEAM ELEcrRIC ELEcrRIC STATION STATION -- 2004 2004 Results in Results in pCi/gm pCi/gm (wet) +/-2S (wet) +/- 2S LOCATION LOCATION SAMPLE TYPE SAMPLE TYPE COLLECTION DATE COLLECTION DATE K*40 OTHER ACTIVITY OTHER ACTIVITY
.. 12F7 12F7 Potato Potato 09/01/04 09/01/04 3.95 :f:.28 3.95 :f:.28 1*25
(( (( (( TABLE J.l3 TABLE J.l3 TYPICA'~ MINIMUM DETECTABLE MINIMUM DETECTABLE CONCENTRATIONS CONCENTRATIONS OF OF NUCLIDES NUCLIDES SEARCHED SEARCHED FOR FOR BUT BUT NOT NOT FOUND FOUND BYBY GAMMA GAMMA SPECTROMETRY SPECTROMETRY IN TIlE IN TIlE VICINITY VICINITY OF OF SUSQUEHANNA SUSQUEHANNA STEAM STEAM ELECTRIC ELECTRIC STATION. STATION. 1004 1004 Fish Fish Sediment Sediment Surface Water Surface Water Ground Water Ground Water Potable Water Potable Water Nuclide Nuclide (pef/g wet) (pef/g wet) (pel/g dry) (pel/g dry) (pCIn) (pCIn) (pCIn) (pCIn) (pCIn) (pCIn) Mn-54 Mn-54 0.019 0.019 0.028 0.028 2.9 2.9 4.1 4.1 1.7 1.7 Co-58 Co-58 0.023 0.023 0.035 0.035 2.1 2.1 4.6 4.6 1.8 1.8 Fe-59 Fe-59 0.050 0.050 0.110 0.110 5.1 5.1 10.2 10.2 8.3 8.3 Co-60 Co-60 0.015 0.015 0.028 0.028 3.3 3.3 5.3 5.3 2.5 2.5 Zn-65 Zn-65 0.028 0.028 0.071 0.071 7.8 7.8 14.4 14.4 6.7 6.7 Zr-95 Zr-95 0.020 0.020 0.070 0.070 6.4 6.4 7.8 7.8 5.4 5.4 Nb-95 Nb-95 N/A N/A N/A N/A 4.3 4.3 5.8 5.8 3.2 3.2 Ru-l03 Ru-l03 N/A N/A N/A N/A 4.9 4.9 5.3 5.3 2.6 2.6 1-131 1-131 0.100 0.100 0.173 0.173 15.4 15.4 8.1 8.1 13.2 13.2 Cs-134 Cs-134 0.010 0.010 0.032 0.032 2.3 2.3 5.2 5.2 2.6 2.6 Cs-137 Cs-137 0.015 0.015 0.033 0.033 2.4 2.4 4.8 4.8 2.5 2.5 8a-140 8a-140 0.300 0.300 0.310 0.310 7.8 7.8 9.0 9.0 9.2 9.2 La-140 La-140 0.040 0.040 0.100 0.100 12.1 12.1 10.1 10.1 10.2 10.2 Ce-141 Ce-141 N/A N/A N/A N/A 6.8 6.8 7.8 7.8 6.8 6.8 Air Particulate Air Particulate Milk Milk FrulUVeg. FrulUVeg. Soli Soli Nuclide Nuclide (E-3 pCi/m3) (E-3 pCi/m3) (peln) (peln) (pel/g wet) (pel/g wet) (pCI/g dry) (pCI/g dry) Mn-54 Mn-54 0.33 0.33 5.5 5.5 0.008 0.008 0.037 0.037 Co-58 Co-58 0.51 0.51 5.1 5.1 0.008 0.008 0.039 0.039 Fe-59 Fe-59 2.31 2.31 12.4 12.4 0.032 0.032 0.993 0.993 Co-60 Co-60 0.28 0.28 5.7 5.7 0.009 0.009 0.055 0.055 Zn-65 Zn-65 0.75 0.75 13.4 13.4 0.025 0.025 0.176 0.176 Zr-95 Zr-95 0.88 0.88 7.7 7.7 0.016 0.016 0.995 0.995 Nb-95 Nb-95 N/A N/A 6.1 6.1 N/A .. N/A 0.071 0.071 Ru-l03 Ru-l03 N/A N/A 5.2 5.2 N/A N/A 0.051 0.051 1-131 1-131 70.3 70.3 8.2 8.2 0.019 0.019 0.097 0.097 Cs-134 Cs-134 0.27 0.27 4.8 4.8 0.OQ7 0.OQ7 0.057 0.057 Cs-137 Cs-137 0.29 0.29 4.4 4.4 0.068 0.068 0.047 0.047 8a-140 8a-140 36.2 36.2 6.7 6.7 0.055 0.055 0.255 0.255 La-140 La-140 11.5 11.5 7.8 7.8 0.016 0.016 0.11 0.11 Ce-141 Ce-141 N/A N/A 8.1 8.1 N/A N/A 0.078 0.078 1-26 1-26
\\
~
APPENDIXJ APPENDIXJ 2004 Radiological 2004 Radiological Em'ironmcntal Em'ironmcntal Monitoring Monitoring Report Report J-l J-l
Appendix J Appendix J The The data data in in the the tables tables that that foll~w show show howhow well well Frarnatome Frarnatome ANP ANP Environmental Environmental Laboratory Laboratory and and Teledyne Brown Teledyne Brown Engineering Engineering Envirorimental Envirorimental SerViCes'(TBE) SerViCes'(TBE) performed performed in in the the analysis analysis of of radioactively spiked radioactively spiked media. Tables J~l through media. Tables through J~5 provide provide the the performance performance results results for for '., FraImitome ANP.' FraImitome ANP.' Tables Tables J.6through J.6through 'J-10'provide
'J-10'provide the the performance performance results results for for TBE.
TBE. In In addition addition to' the to' the AnaI.Ytjcs~spikes analyz.ed analyz.ed as as part part ofPPL'sREMP ofPPL'sREMP Laboratory Laboratory Spike Spike Piogrrim Piogrrim (Tables (Tables J-3 J-3 and J-8);Framatome and J-8);Framatome ANP ANP and and TBETBE analyzed analyzed spikes spikes procured procured independently independently from from Analytics Analytics asas part of part of their their resp'ective resp'ective Quality Quality Control Control Spike Spike ProgramsPrograms (Tables (Tables J-2 J-2 and and J-7),J-7), as as wellas wellas spikes spikes prepared a's prepared a's part part ofof the the following following prognlriis: prognlriis: ".:, ".:, 'I::'" 'I::'"
- 1. The
- 1. The Proficiency Proficiency TestingTesting Program Program 'of 'of Enviri:;riinentiResource Enviri:;riinentiResource Associates Associates (Tables (Tables J-l and 1-6)
J-l and 1-6) ,,
- ** 11 ~ >> ~: ~ :: <.!. 01.
<.!. 01.
- 2. The
- 2. Qua1ity Assessment The Qua1ity Assessment ProgramProgram of of DOE's DOE's Environmental Environmental Measurements Measurements Laboratory Laboratory (EML)
(EML)
,, (Tables (Tables 1-4, 1-4, and and 1-9) 1-9) "" ;; ~ "" .' .' .:.: ..
- 3. The
- 3. Mixed Analyte The Mixed Analyte Performance Performance Evaluation Evaluation Program Program (MAPEP)
(MAPEP) of of the the DOE DOE (Tables(Tables 1-5 1-5 and, and, 1-10) 1-10) It should be It should be noted noted thatthat program program #1 #1 above'only above'only provides provides spiked spiked water water for for analyses. analyses. 'No 'No other other ... media are media are included included in in the the spikes spikes provided provided by by thisthis program.program. Also, Also, itit should should be be noted noted that that the the levels of levels of activity activity in in spikes spikes ofof different different media media prepared prepared for for program program #2 #2 tend tend to to be: be: relatively relatively high. high. They are They are relatively relatively high high compared compared to to the the levels levels of of activity activity in in the the spikes spikes prepared prepared by by Analytics Analytics as as part of part of its its Environmental Environmental Cross Cross Check Check Program Program and and for for PPL's PPL's REMP REMP Laboratory Laboratory Spike Spike Program. Program. The following The following characteristics characteristics are are important important for for the the spiked spiked environmental environmental media: media:
- 1. When
- 1. practical, the When practical, the level level of of activity activity in.
in. atat least, least, some some ofof the the spiked spiked environmental environmental media media
,, should should be be within within thethe range range between between required required analysis analysis sensitivities sensitivities for for the the SSES SSES REMPREMP and and the Reporting the Reporting Levels,Levels, if applicable, of if applicable, of the the NRC. NRC.
- 2. The
- 2. spikes should The spikes should be be preserved preserved in in aa manner manner as as similar similar as as possible possible to to thethe way way that that actual actual samples of samples those media of those media areare prepared.
prepared.
- 3. The
- 3. variety of The variety of radionuclides radionuclides with with which which environmental environmental media media areare spiked spiked should should be be as as extensive as extensive as practica1, practica1, incJuding incJuding as as many many as as of of thethe activation activation and and fission fission products products that that cou1d cou1d be detected be detected in in the the vicinity vicinity of of the the SSES SSES as as reasonable.
reasonable. The spiked environmental The spiked environmental media media prepared prepared by by Analytics Analytics according according to to the the requirements requirements of of PPL's PPL's REMP Laboratory REMP Laboratory Spike Spike Program Program are are intended intended to to incorporate incorporate characteristics characteristics #1, #1, #2,
#2, and and #3
#3 toto the the greatest degree greatest degree that that isis practical.
practical. 2004 Radiological 2004 Radiological Environmental Environmental Monitoring Monitoring Report Report :: J-2 J-2
AppendixJ The criteria for The criteria for the the acceptability acceptability ofof the the analyses analyses results results for for the spikes prep~d as the spikes as part part of of the the PPL PPL REMP Laboratory REMP Laboratory Spike Spike Program Program (Tables (Tables 1-3 & 1-~) have 1-3 & have been been established established by by PPL. PPL. They They are are \..-:
\..-:
based on based on criteria criteria that that were were originally originally developed developed by by the the NRC. NRC. TheThe NRC NRC bases bases these these criteria criteria on on an an empirical relationship empirical relationship that that combines combines prior prior experience experience and and accuracy accuracy neeqs. neeqs. As As the the resolution resolution of of the measurement the measurement process process improves improves (relative uncertainty becomes (relative meas~rement uncertainty becomes smaller), smaller), the the criteria for criteria for detennining detennining acceptability acceptability become become tighter. ,Conversely, as tighter. ,Conversely, as the the resolution resolution of of the the process process becomes poorer becomes poorer (relative (relative measurement measurement uncertainty becomes bigger), uncertainty becomes bigger), the the criteria criteria are are widened. widened. The criteria for The criteria for acceptability acceptability ofof DOE DOE programs programs (EML's (EML's and and MAPEP's MAPEP's programs programs -- Tables Tables 1-4, I-1-4, I-5,1-9 and 5,1-9 and 1-10) are based 1-10) are based onon control control limits limits based based onon percentiJes percentiJes of of historic historic data data distributions. distributions. Note that Note that comment comment numbers numbers at at the the extreme extreme right right side side of of the the tables tables denote denote unacceptable unacceptable results results in in Tables through 1-10. 1-1 through Tables 1-1 Discussions relevant 1-10. Discussions relevant to these comment to these comment numbers numbers follow follow the the presentations of presentations of the the data, as applicable. data, as applicable. Radionuclide concentration results Radionuclide concentration not available results not available (due (due to to curdled curdled milk milk sample, sample, not not acceptable acceptable for for gamma and gamma and I-l3Ilow I-l3Ilow level level analysis) analysis) and and therefore therefore not not included included in in Table Table 1-8 1-8 for for the the folJowing: folJowing: Analytics Sample Analytics Sample Number: Number: E4307-186 E4307-186 (spiked (spiked milk). milk). J-3 J-3 2004 Radiological 2004 Radiological Environmental Environmental Monitoring Monitoring Rep~rt
TABLEJ*l ENvrnONMENTAL ENvrnONMENTAL RESOURCE RESOURCE ASSOCIA ASSOCIATES TES (E~A) ** PROFICIENCY TESTING PROFICIENCY TESTING PROGRAM PROGRAM -- 2004 2004 FRAMATOME ANP FRAMATOME ANP ENvrnONMENTAL ENvrnONMENTAL SERVICES SERVICES LABORATORY LABORATORY (page 1 (page 1 of2) of2) Identmcatlon Identmcatlon ERA Known ERA Known Framatome Framatome FramatomelERA FramatomelERA ERA ERA MonthlYear MonthlYear No. No. Medium Medium Units Units Nuclide Nuclide Result (a) Result (a) Results (a) Results (a) Ratio Ratio Control LImits (b) Control LImits (b) Evaluation Evaluation May-04 Rad-S7 Water pCiJI Gross Alpha 38.8 34 0.88 22.0-55.6 Acceptable pCin Gross Beta 59.6 57.8 0.97 42.3*76.9 Acceptable pCiJI Tritium 30900 31200 1.01 25600-36200 Acceptable pCiJI Ba-133 101 98.6 0.98 83.5*118 Acceptablo pCiJI Cs*134 50.5 49.8 0.99 41.8-59.2 Acceptable pCiJI Cs*137 82.5 82.4 1.00 73.8-91.2 Acceptable pCiJI Co-60 41.6 40.5 0.97 32.9-50.3 Acceptable pCiJI Zn-6S 75.2 75.6 1.01 62.2-88.2 Acceptable* pCiJI 1-131 25.1 26.4 *1.05 19.9-30.3 Acceptable November-04 Rad*S9 Water pCiJI Gross Alpha 31.7 27.7 0.87 18.0-45.4 Acceptable pCiJI Gross Beta 36.3 32.9 0.91 27.6-45.0 Acceptable pCiJI Tritium 20700 21300 1.03 . 17100*24300 Acceptable pCin Ba*133 78.4 76.3 0.97 64.8*92.0 Acceptable pCiJI Cs*134 42.9 42.4 0.99 34.2-51.6 Acceptable pCiJI Cs*137 60.1 61.2 1.02 51.4*68.8 Acceptable pCiJI Co-60 11.7 116 9.91 3.04-20.4 (1) pCiJI Zn*65 50.9 52 1.02 42.1-59.7 Acceptable pCiJI . 1-131 *22.1 20.2 0.91 16.9-27.3 Acceptable (a) Results (a) Results are are the the average average of of three three measurements, measurements, reported reported in in units units of of pCiJI. pCiJI. Per guidelines (b) Per (b) guidelines of of the the EPA'S EPA'S National National Standards for Water Standards for Water Proficiency Proficiency Testing Testing Criteria Criteria Document. Document. December December 1998. 1998. J-4 J-4
TABLEJ-l TABLEJ-l ENVIRONMENTAL RESOURCE ASSOCIATES ENVIRONMENTAL RESOURCE ASSOCIATES (ERA) (ERA) PROFICIENCY TESTING PROFICIENCY TESTING PROGRAM PROGRAM -- 2004 2004 FRAMATOME ANP FRAMATOME ANP ENVIRONMENTAL ENVIRONMENTAL SERVICESSERVICES LABORATORY LABORATORY (Page2of2) (Page2of2) COMMENTS COMMENTS
..Analyzed Analyzed value value of of 11.6 11.6 pCiIl pCiIl was was entered entered into into ERA ERA database database as as 116 116 pCiIl.
pCiIl. J-S (( J-S
TABLEJ-2 TABLEJ-2 ANALYTICS ANAL YTICS ENVIRONMENTAL ENVIRONMENTAL RADIOACTIVITY RADIOACTIVITY CROSS CROSS CHECK CHECK PROGRAM PROGRAM -- 2004 2004 FRAMATOME ANP FRAMATOME ANP QUALITY QUALITY CONTROL CONTROL SPIKE SPIKE PROGRAM PROGRAM FRAMATOME ANP FRAMATOME ANP ENVIRONMENTAL ENVIRONMENTAL LABORATORY LABORATORY (page 1 of 6) Analytlcs Framatomel Identification Calculated Framatome Analytlcs QuarterNear No. Medium Units Nuclide Results Results Ratto 1sV04 E4061-1G2 Milk pCiIl 1-131LL* n.7 83.G 1.08 pCiIl 1-131 n.7 n.73 1.00 pCiIl Ce-141 85.2 92 1.08 pCIII ' Cr-51 327 314 0.96 pCiIl Cs-134 90 88.7 0.99 pCIII Cs-137 . 185 188.6 1.*02 pCiIl Co-58 112 115 1.03 pCiIl Mn*54 114 114.7 1.01 '
-~.~ pCiIl Fe-59 56.8 59.7 " 1:05 pCiIl Zn*65 143 145.5 1.02 pCiIl, Co-SO 153( 154.8 1.of
~ , '~
lsV04 E4057-162 Water pCiIl Gr:Alpha 74.5 72.3: 0.97 pCiIl ' Gr. Beta 301 ' 285.7 0:95 lsV04 E4058-162 Water pCiIl 1-131, 90.2 94 ' 1.04 pCiIl 1-131LL* 90.2 88,7' 0.98 pCiIl Ce-141 85 87.5 1.03 pCIII Cr-S1 326 335 1.03 pCIII' Cs-134' 89.7 86 0.96 pCIII Cs-137 185 185.6 1.00 pCIII Co-58 ; 112 113.2 1.01 pCiIl. Mn-54 114 112.3 0.99 pCiIl Fe-59 56.7 60.8* 1.07
-, - pCiIl Zn-65 143 149.1.. 1.04 pCiIl Co-GO* 153 151.4 0.99 lsV04 E4059-162 Water pCiIl Sr-89 I 123 107.7 0.88 pCiIl Sr-90 14.5' 14.85 1.02 lsV04 E4060*162 AP Filter pCi' ' :' Gr. Alpha I 58.9 48.09 0.82 pCI
. , Gr. Beta 218 231.1 1.06
, j r
!'": '; " ..' ( l : j'
- 1-131 LL = radiochemical LL = radiochemical separation separation analysis analysis J*6
TABLEJ*2 ANALYTICS ANAL YTICS ENVIRONMENTAL ENVIRONMENTAL RADIOACTIVITY RADIOACTIVITY CROSS CROSS CHECK CHECK PROGRAM - 2004 2004 FRAMATOME ANP FRAMATOME ANP QUALITY QUALITY CONTROL CONTROL SPIKE SPIKE PROGRAM PROGRAM FRAMATOME ANP FRAMATOME ANP ENVIRONMENTAL ENVIRONMENTAL LABORATORY LABORATORY 2 of (page 2 (page 6) of 6) AnaJytlcs Framatomel Identification Calculated Framatomo Analytlcs OuarterNear No. Medium Units Nuclide Results Results Ratio 151104 E406H62 Milk pCiII 1-131 77.7 77.73 1.00 pCiII 1-131ll* 77.7 83.6 .1.08 pCiII Ce-141 85.2 92 1.08 pCiII Cr~51 327 314 0.96 pCiII Cs-l34 90 88.7 0.99 pCiII C5-137 185 188.6 1.02 pCiII Co-58 112 115 1.03 pCiII Mn-54 114 114.7 1.01 pCiII Fe-59 56.8 59.7 1.05 pCiII Zn-65 143 145.5 1.02 pCiII C0-60 153 154.8 1.01 151104 E4062*162 Milk pCiII Sr-89 103 86.2 0.84 pCiII Sr-90 12.1 12.7 1.05 2ndI04 E4182-162 Water pCiII H-3 11900 11680 0.98 2ndlO4 E4183-162 AP Filler pCi Gr. Alpha 48.8 46.8 0.96 pCI Gr. Beta 160 156 0.98 31 LL =
=
LL radiochemical radiochemical separation separation analysis analysis c
- 1-) 31 1-7 c ((
(( TABLEJ*2 ANALYTICS ANAL YTICS ENVIRONMENTAL ENVIRONMENTAL RADIOACflVITY RADIOACflVITY CROSS CROSS CHECK CHECK PROGRAM PROGRAM -- 2004 2004 FRAMATOME ANP FRAMATOME ANP QUALITY CONTROL SPIKE QUALITY CONTROL SPIKE PROGRAM; PROGRAM; FRAMATOME ANP FRAMATOME ANP ENVIRONMENTAL ENVIRONMENTAL LABORATORY LABORATORY (page 3 (page of 6) 3 of 6) :: Analytlcs Framatomel Identification Calculated Framatome Analytlcs QuarterNear No. MedIum Units Nuclide Results Results Ratio 2nd/04 E4184A-162 Filter pCI Ce-141 88.3 86 0.97 pCI Cr-51 128 127 0.99 pCI Cs*l34 56.9 54 0.95 pCI 'Cs-137 87.8 90 1.03 pCI Co-58 26 27 1.04 pCI' Mn-54 39.7 '42 1.06
.' , pCI Fe-59 25.1 27 1.08 pCI' Zn-65 56 62 1.11 p~1 Co-60 ....'1 96.8 92 0.95
;:",,:- ~ i ~ ;. "
2ndlO4 E4185-162 Alter, pCI Sr-89 (1) pCI Sr-90 (1) 2nd/04 E4186-162 Milk pCiII 1-131 58.2 55 0.95 pCill r*131ll* 58.2 59 1.01 pCiII Ce-141 157 165 1.05 pCiII Cr-51 228 241 1.06 pCiII CS-l34 101 99 0.98 pCiII Cs-137 156 157 1.01 pCiII Co-58 46.2 46 1.00 pCiII Mn-54 70.5 73 1.04 pCiII ' Fe-59 44.5 48 1.08 pCiII ' Zn-65 99.3 100 1.01 pCiII . Co-SO 172 175 1.02
,I,
,I,
- 1-131 LL =radiochemical LL =radiochemical separation separation analysis analysis J-8
TABLEJ*2 ANALYTICS ANAL YTICS ENVIRONMENTAL ENVIRONMENTAL RADIOACTIVITY RADIOACTIVITY CROSS CROSS CHECK CHECK PROGRAM PROGRAM -- 2004 2004 FRAMATOME ANP FRAMATOME ANP QUALITY QUALITY CONTROL CONTROL SPIKESPIKE PROGRAM PROGRAM FRAMATOMEANPENVIRONMENTALLABORATORY FRAMATOMEANPENVIRONMENTALLABORATORY (Page 44 of (Page of 6) 6) Analytics Framatomel Identification Calculated Framatome Analytlcs auarterNear No_ Medium Units Nuclide Results Results Ratio 3rdlO4 E4269-162 Water pCi/I Gr. Alpha 42.7 41.3 0.97 pCi/I Gr. Beta 225 214 0.95 3rdlO4 E427()'162 Water pCW 1-131LL" 70.8 67.8 0.96 pCW 1*131 70.8 70.5 1.00 pCW Ce*141 250 258 1.03 pCW Cr-51 223 230 1.03 pCi/I Cs-134 96.4 93.4 0.97 pCi/I Cs-137 215 217 1.01 pCi/I Co-58 94.6 93.4 0.99 pCi/I Mn-54 181 181 1.00 pCi/I Fe-59 91.6 95.2 1.04 pCW Zn-65 178 180 1.01 pCi/I Co-GO 125 126 1.01 3rdlO4 E4271-162 APFilter pCi Gr. Alpha 36.8 38.3 1.04 pCI Gr. Beta 194 191 0.96 3rdlO4 E4272-162 Milk pCW 1-131LL" 83.5 79.4 0.95 pCW '-131 83.5 81.1 0.97 pCW Ce-141 235 240 1.02 pCW Cr-51 210 214 1.02 pCW Cs-l34 90.6 89.5 0.99 pCW Cs-137 202 204 1.01
'pCW Co-58 89 90.9 1.02 pCW Mn-S4 171 173 1.01 pCW Fe-59 86.1 91.3 1.06 pCi/I Zn*65 167 169 1.01 pCi/I Co-50 118 116 0.98 3rd104 E4273-162 Milk pCi/I Sr-89 102 99.2 0.97 pCi/I Sr-90 24.5 23.4 0.96 3rdl04 E434()'162 Filter(2) pCI Sr-89 .152 151 0.99 pCI Sr:90' 58.8 53.5 0.91
- 1-131 u.. =radiochemical radiochemical separation separation analysis analysis
(. (" J-9
c' (" (. TABLEJ.2 ANALYTICS ANAL YTICS ENVIRONMENTAL ENVIRONMENTAL RADIOACTIVITY RADIOACTIVITY CROSS CROSS CHECK CHECK PROGRAM PROGRAM -- 2004 2004 FRAMATOME ANP FRAMATOME ANP QUALITY QUALITY CONTROL CONTROL SPIKE SPIKE PROGRAM PROGRAM FRAMATOMEANPENVIRONMENTALLABORATORY FRAMATOMEANPENVIRONMENTALLABORATORY (page 5 of 6) Analytlcs Framatomel Identlf1catlon Calculated Framatome Anatyttcs QuarterNear No. Medium Units Nucflde Results Results Ratio 4thl04 E4380-162 Water pCIII H-a 8060 8327 1.03 4thlO4 E4381*162 . Filter pCI Sr-89 92.3 87.7 0.95 pCI Sr-90 10,6 8.78 0.83 4thl04 E4382*162 Filter pCI Gr.Alpha 29.5 24.9 0.84 pCI Gr. Beta 204 223 1.09 4thl04 E4383*162 Filter pCI Ce*141 80.3 75.6 0.94 pCI Cr-51 189 201 1.06 pCI Cs-134 84.7 82.4 0.97 pCI Cs-137 62.9 68.8 1.09 pCI Co-58 72.9 75.3 1.03 pCI Mn-54 67.7 76.3 1.13 pCI Fe-59 60.5 69.8 1.15 pCI Zn-65 97.7 109 1.12 pCi Co-60 87.1 85.1 0.98
'4thlO4 E4384-162 Milk pCIII 1-131ll* 66,7 64.2 0.96 pCIII '-131 66.7 69,0 1.03 pCIJI Ce*141 155 154 0.99 pCIJI Cr-51 379 385 1.02 pCIII C5*134 170 167 0.98 pCIJI Cs-137 126 132 1.05 pCIJI Co-58 146 147 1.01 pCIJI Mn-54 136 144 1.06 pCIJI 'Fe-59 121 129 1.07 pCIJI Zn-65 196- 197 1.01 pCIJI C0-60 175 In 1.01 4thl04 . E4412-162 Water, . pCIII' o Sr-89.' "98.1 . 90.9' 0.93 pCIJI Sr*90 11.3 9.33 0.83
- 1*131 LL = radiochemical LL = radiochemical separation separation analysis analysis 1*10
TABLEJ*2 ANALYTICS ANAL YTICS ENVIRONMENTAL ENVIRONMENTAL RADIOACTIVITY RADIOACTIVITY CROSS CROSS CHECK CHECK PROGRAM PROGRAM -- 2004 2004 FRAMATOME ANP FRAMATOME ANP QUALITY QUALITY CONTROL CONTROL SPIKE SPIKE PROGRAM PROGRAM FRAMATOMEANPENVIRONMENTALLABORATORY FRAMATOMEANPENVIRONMENTALLABORATORY (page of 6) (page 66 of 6) COMMENTS
. COMMENTS (1)
(1) Problems encountered Problems encountered in in filter dissolution. filter filter dissolution. filter re*ordered. (2) (2) Replacement filter Replacement filter for for lost lost 2nd2nd quarter quarter filter. filter. J-ll ( ( (
(' ( TABLEJ-3 TABLEJ-3 PPL REMP lABORATORY PPL REMP lABORATORY SPIKE SPIKE PROGRAM PROGRAM ANALYI1CS ENVIRONMENTAL ANALYI1CS ENVIRONMENTAL RADIOACTIVITY RADIOACTIVITY CROSS CROSS CHECK. CHECK. PROGRAM* 20042004 FRAMATOME ANP FRAMATOME ANP ENVIRONMENTAL ENVIRONMENTAL lABORATORY lABORATORY (page loCS) (page loCS) Identification Analytic. Framatome FramatomelAnalytlcs MonthIYear No. Medium Units Nuclide Calculated Results (a} Results (a} Ratio March*04 E4073.186 Sediment, pCilkg Ce-141 150:1: 5 157:1: 15 1.05 pCilkg Cr-S1 576:1: 19 586:1: 42 1.02 pCVkg Cs*134 159:1: 5 160':1: 6 1.01 pCilkg Cs-137 432:1: 14 452 :1:9 1.05 pCilkg CO-58 198 :1:7 195 :1:7 0.98' pCilkg Mn*54 201:1: 7 191 :I: 12 0.95 pCilkg Fe-59 100 :1:3 107:1: 8' 1.07 pCilkg Zn*65 252 :1:8 261 :I: 11 1.04' pCilkg Co-GO, 270 :1:9 268 :1:'6 0.99 March-04 E4069-186 Milk pCiII /*131 .' . 91 £3 88-~3 0:97 pClIl 0e-141 ' 95:ti3' ; 98':t'4 1.03 pblll Cr*S1 363 :1:'12 37!f:l:26 f.03 pClIl Cs-134 100 :1:3 95 :1:4 0.95 pCiII Cs~137 206 :7 208 :1:'6' 1:01 pClIl Co-58 125':4 128:1:'5 1.02 pClIl Mn*54 ' 127: 4 130:1: 5 1.02 pCiII Fe-59 63 :1:2 64:1: 6 1.02 pClIl Zn*65 159: 5 163:1: 9 1.03 pClIl. Co-GO 170 :1:6 168 :t 4 0.99
, I March*04 E4070*18G AP Filter pCl Ce-141 72 :1:3 65 :1:1 0'.90 pCl Cr*51 278: 10 267:1: 10 0.97 pCl Cs*134 76 +/-3 69 +/- f .... ,-, 0.91
, '. ~
pCl Cs-137 157 +/-5 157:t 2 1.00 pCl Co-58 95 :1:3 94:1:2 0.99' pCl Mn-54 97 :3 98 :1:2 1.01 pCl Fe-59'. ' 48 :1:2 53 :t 2 1.10
, -pCl Zn*65 ';' 121 +/- 4 121 :t 4 1.00 pCl' ,Co-GO
. 130:1: 5 119:1: 2 0.92 (a) Counting (a) Counting error error is is two two Itftndru-d Itftndru-d deviations.
deviations. 1*12
TABLEJ-3 TABLEJ-3 PPL REMP LABORATORY PPL REMP LABORATORY SPIKE SPIKE PROGRAM PROGRAM ANALYTlCS ANAL YTlCS ENVIRONMENTAL ENVIRONMENTAL RADIOACTIVlTY RADIOACTIVlTY CROSSCROSS CHECK CHECK PROGRAM PROGRAM -- 2004 2004 FRAMATOME ANP FRAMATOME ANP ENVIRONMENTAL ENVIRONMENTAL LABORATORY LABORATORY (Page 2ofS) (Page 2ofS) Identification Anelytlcs Framatome FrametomeJAnalytics MonthIYeer No. Medium Units Nuclide Caloulated Results (a) Resulls(a) Ratio March*04 E4071-186 AP FUter pCI Ce-141 79 :3 73: 1 0.92 pCl Cr-51 301 :I: 11 290 :9 0.96 pCl Cs134 83 :1:3 75: 1 0.90 pCl Cs-137 171: 6 173 :3 1.01 pCI Co-58 104: 4 102: 2 0.98 pCI Mn-54 105: 4 106:1: 2 1.03 pCI Fe-59 52 :2 57:t 2 1.10 pCl Zn-55 132 :t 5 139:1: 4 1.05 pCI Co-GO 141: 5 126 :1:2 0.91 March-D4 E4072*186 AP Filter pCI Ce-141 78 :3 65: 1 0.83 pCl Cr*51 300:11 259: 9 0.86 pCI Cs-134 83: 3 59 :t 1 0.83 pCl Cs-137 170 +/- 6 155: 2 0.91 pCl Co-58 103: 4 92: 2 0.89 pCl Mn-54 105: 4 97: 2 0.92 pCl Fe-59 52:t 2 49 :t 2 0.94 pCl Zn-G5 131 :t 5 125 :t 4 0.95 pCI Co-60 141:t 5 116 ":t 2 0.82 June-04 E4205-186 Charcoal Filler pCI 1-131 90 :3 r- 97 :1:3 1.07 June-04 E420G-186 Charcoal Filter pCl 1*131 83 :3 90 :1:3 1.09 June-04 E4207-186 Charcoal Filter pCl 1-131 76-:1:3 87:t 3 1.13 (a) (a) C is two
":ug mot is two ltaudatd deviations.
ltaudatd deviations. J*13 rr
c TABLEJ-3 TABLEJ-3 PPL REMP LABORATORY PPL REMP LABORATORY SPIKE SPIKE PROGRAM PROGRAM ANALYTICS ENVIRONMENTAL ANALYTICS ENVIRONMENTAL RADIOACllVTl'Y RADIOACllVTl'Y CROSS CROSS CHECKCHECK PROGRAM PROGRAM -- 2004 2004 FRAMATOMB ANP FRAMATOMB ANP ENVIRONMENTAL ENVIRONMENTAL LABORATORY LABORATORY (page 3 (page 3 of5) of5) Identlfioatlon Analytlcs Framatonle FramatomelAnalytlcs MonthNeer No. Medium Units Nuclide Calculated Results (a) Results (8) Rallo September.04 E4311-186 Milk pClII 1-131 76 :t:3 82:t: 17 1.08 pClII Ce-141 518:1: 17 50S :t: 10 0.98 pClII Cr*51 463 :t: 15 481 :t: 47 1.04 pClII CS-134 200 :t:7 197 :t:6 0.99 pClII CS-137 445 :t: 15 448:t:8 1.01 pClII Co-58 196 :1:7 195:t: 6 0.99 pClII Mn*54 376:1: 13 388:t:8 1.03 pClII Fe-59, 190:1: 6 199 :1:8 1.05 pClII Zn*65 ' 370 :1:12 374 :1:'13 1.01 ' pClII Co-60 260 ':t:9,' 261:1: 5 ' 1.00 '
.. .:' <, .. . .. ~
. September.04 E4312-f86 Charcoal Filler pCl 1-131 75 :t:3 82 :1:6 1.09 Seplember*04 E4313-186 Charcoal FIller PCI 1-131 ' 83':1:3 95:1:6' 1.14 September.04 E43f4-186 Charcoal FIlter pCl 1-131 70 :1:2 82 :1:6* 1.17' Oetober*04 E4342-186 Milk pClII 1-131 79 :1:3 76:1: 14 0.96 pClII Ce-141 89 :1:3 95:1: 13 1.07 pClII Cr-51 ' 2790:1: 93 2870:1: 130 1.03 pClII C$o134 69 :t:2 62':1:9 0,90 .
pClII C$o137 158:1: 5 150:1: 13 0.95 pClII Co-58 50 +/-2 42':1:9 0.84 pClII Mn-54 124 +/-4 124:t: 12 1.00 pClII Fe-59 40:t: 1 .. 37 +/- 13 ' 0,93 pClII Zn-65 119 ;t 4 ' 109 :1:21 " 0.92 pCliJ CO-60 91 +/-3 84 :t:8 0.92 I Counting error (II) Counting (II) error is is two two standard standard deviations. deviations. J-14
TABLEJ-l TABLEJ-l PPL REMP lABORATORY PPL REMP lABORATORY SPIKE SPIKE PROGRAM PROGRAM ANALYTICS ENVIRONMENTAL ANALYTICS ENVIRONMENTAL RADIOAcnVITY RADIOAcnVITY CROSS CROSS CHECKCHECK PROGRAM PROGRAM -- 2004 2004 FRAMATOMBANP ENVlRONMENTALLADORATORY FRAMATOMBANP ENVlRONMENTALLADORATORY (pagc4ofS) (pagc4ofS) Identification Identification Analytlcs Analytlcs Framatome Framatome FramatomelAnalytios FramatomelAnalytios MonthlYear MonthlYear No. No. Medium Medium Units Units Nuclide Nuclide Calculated Results (a) Calculated Results (a) Results (a) Results (a) Ratio Ratio December-04 December-04 E4417-185 E4417-185 Milk Milk pCi/I pCi/I 1-131 1-131 71 :t:2 71 :t:2 65 :t:9 65 :t:9 0.92 0.92 pCi/I pCi/I Ce-141 Ce-141 167 :t:8 167 :t:8 154:t: 154:t: 66 0.98 0.98 pCi/I pCi/I Cr-51 Cr-51 410 :t: 410 :t: 21 21 392:t:36 392:t:36 0.96 0.96 pCi/I pCi/I Cs-134 Cs-134 184 :t:9 184 :t:9 173 :t:6 173 :t:6 0.94 0.94 pCi/I pCi/I Cs-137 Cs-137 136 ;t 136 ;t 77 137 :t:5 137 :t:5 1.01 1.01 pCi/I pCi/I Co-58 Co-58 158:t: 88 158:t: 152 :t:5 152 :t:5 0.96 0.96 pCi/I pCi/I Mn-54 Mn-54 147 :t:7 147 :t:7 152 :t:5 152 :t:5 1.03 1.03 pCi/I pCi/I Fe-59 Fe-59 131 :: 77 131 132 ;t 132 ;t 77 1.01 1.01 pCi/I pCi/I Zn-65 Zn-65 212 :t: 11 212 :t: 11 204:t: 10 204:t: 10 0.96 0.96 pCi/I pCi/I C0-60 C0-60 189 :t:9 189 :t:9 185 :4 185 :4 0.98 0.98 December-04 December-04 E4418-185 E4418-185 AP Filter AP Filter pCl pCl Ce-141 Ce-141 70 :2 70 :2 63 63 :t:3
- t:3 0.90 0.90 pCi pCi Cr-51 Cr-51 165:t: 66 165:t: 152 152 :t: 19
- t: 19 0.98 0.98 pCl pCl Cs-134 Cs-134 74;t 33 74;t 66 66 :3
- 3 0.89 0.89 pCl pCl Cs-137 Cs-137 55;t 22 55;t 56 56 :4
- 4 1.02 1.02 pCi pCi Co-58 Co-58 64 :t:2 64 :t:2 64 64 :t:4
- t:4 1.00 1.00 pCi pCi Mn-54 Mn-54 59 :2 59 :2 60 60 :t:4
- t:4 1.02 1.02 pCl pCl Fe-59 Fe-59 53 :t:2 53 :t:2 57 57 :t:5
- t:5 1.08 1.08 pCl pCl lo-65 lo-65 85 :3 85 :3 93 93 :t:8
- t:8 1.09 1.09 pCl pCl C0-60 C0-60 76 :t:3 76 :t:3 67 67 :3
- 3 0.88 0.88 December*04 E4419-186 E4419-186 .. AP AP Filter Filter pCl pCl Ce-141 Ce-141 77 :t:3 77 :t:3 67 :t:3 67 :t:3 0.B7 0.B7 pCl pCl Cr-51 Cr-51 182:t: 66 182:t: 193 :t: 18 193 :t: 18 1.06 1.06 pCl pCl Cs-134 Cs-134 82 :t:3 82 :t:3 76 :t:3 76 :t:3 0.93 0.93 pCi pCi CS-137 CS-137 61 ;t 61 ;t 22 62 :t:4 62 :t:4 1.02 1.02 pCl pCl Co-58 Co-58 70 :t:2 70 :t:2 68 :t:4 68 :t:4 0.97 0.97 pCl pCl Mn-54 Mn-54 65 :t:2 65 :t:2 67 :t:4 67 :t:4 1.03 1.03 pCl pCl Fe-59 Fe-59 58 :t:2 58 :t:2 64 :t:5 64 :t:5 1.10 1.10 pCi pCi Zn-65 Zn-65 94:t: 33 94:t: 106:t: 8 106:t: 8 1.13 1.13 pCl pCl C0-60 C0-60 84 :t:3 84 :t:3 75 :t:3 75 :t:3 0.89 0.89
(( (a) 0- "'iog (a) 0- error is
"'iog error is two two standard standard deviation&.
deviation&. I-IS I-IS (,(, rr
(( TARLEJ*3 PPL REMP LABORATORY PPL REMP LABORATORY SPIKESPIKE PROGRAM PROGRAM ANALY11CS ANAL Y11CS ENVIRONMENTAL ENVIRONMENTAL RADIOAC11VITY RADIOAC11VITY CROSSCROSS CHECK CHECK PROGRAM* 20042004 FRAMATOME ANP FRAMATOME ANP ENVIRONMENTAL ENVIRONMENTAL LABORATORY LABORATORY (page S o(5) (page S o(5) Identification Identification Analytlcs Analytlcs Frematome Frematome FramatomalAnalytlos Framatomal Analytlos MonthlVear MonthlVear No. No. Medium Medium Units Units Nuclide Nuclide Calculated Calculated Results (8) Results (8) Results (a) Results (a) Ratio Ratio Oeeemoor-04 Oeeemoor-04 E4420-186 E4420-186 AP Filter AP Filter pCl pCl Ce-141 Ce-141 101 101 :t 4
- t 4 91 :t:
91 :t: 4 4 0.90 0.90 pCl pCl Cr-S1 Cr-S1 237 237 :t:8
- t:8 224:t: 21 224:t: 21 0.95 0.95 pCl pCl CS-134 CS-134 106 106 :t 4
- t 4 94 :1:3 94 :1:3 0.89 0.89 pCl pCl CS-137 CS-137 79 79 :1:3
- 1:3 79 :1:4 79 :1:4 1.00 1.00 pCl pCl Co-58 Co-58 92 92 :1:3
- 1:3 91:1: 4 91:1: 4 0.99 0.99 pCl pCl Mn-54 Mn-54 85 :1:3 85 :1:3 91 :I:
91 4
- I: 4 1.07 1.07 pCI.
pCI. Fe-59 Fe-59 76 :1:3 76 :1:3 85 :t:5 85 :t:5 1.12 1.12 pCl pCl Zn-65 Zn-65 123 :t 123 4
- t 4 136 :1:9 136 :1:9 1.11 1.11 pCl pCl C0-60 C0-60 109 :t:4 109 :t:4 102:1: 4 102:1: 4 0.94 0.94 (a) Counting (a) Counting error error is is two two ltlloolU'd ltlloolU'd deviations.
deviations. J-16 J-16
(( (( (( TABLEJ-4 TABLEJ-4 DOE -- ENVIRONMENTAL DOE ENVIRONMENTAL MEASUREMENTS MEASUREMENTS LABORATORY LABORATORY (EML) (EML) QUALITY ASSESSMENT QUALITY ASSESSMENT PROGRAM PROGRAM (QAP) (QAP) FRAMATOME ANP FRAMATOME ANP ENVIRONMENTAL ENVIRONMENTAL LABORATORY LABORATORY (Page 1 (Page 1 of of 1) 1) Identification Identification EMLKnown EMLKnown Framatome Framatome FramatomelEML FramatomelEML MonthNear MonthNear No. No. MedIum MedIum Units Units NuclJde NuclJde Results Results Results Results Ratio Ratio March-04 March-04 QAP60* Soil Soil 8q1kg 8q1kg K-40 K-40 539 539 596 596 1.11 1.11 Soil Soil 8q1kg 8q1kg Sr-gO Sr-gO 51 51 47 47 0.92 0.92 Soil Soil Bqlkg Bqlkg Cs-137 Cs-137 1323 1323 1515 1515 1.15 1.15 Soil Soil 8qlkg 8qlkg Ac-Th-228 Ac-Th-228 49 49 51 51 1.03 1.03 Vegetation Vegetation 8q1kg 8q1kg K-40 K-40 720 720 752 752 1.04 1.04 Vegetation Vegetation Bqlkg. Bqlkg. Co-60 Co-60 14 14 15 15 1.03 1.03 Vegetation Vegetation Bqlkg Bqlkg Cs-137 Cs-137 585 585 593 593 1.01 1.01 Water Water BqJI BqJI H-3 H-3 187 187 219 219 1.17 1.17 Water Water Bq/I Bq/I Co-60 Co-60 163 163 154 154 0.94 0.94 Water Water 8qn 8qn Cs-137 Cs-137 52 52 48 48 0.93 0.93
- EML has
- EML has notified notified the the industry industry that that QAP QAP 60 60 (March (March 2004) 2004) was was the the final final set set or or samples samples to to be be issued.
issued. J-t7 J-t7
( ( ( TABLEJ*5 DOE -- MAPEP DOE MAPEP -- 04*12 MIXED ANALYTE MIXED ANALYTE PERFORMANCE PERFORMANCE EVALUATION EVALUATION PROGRAM PROGRAM FRAMATOMEANPENVmONMENTALLABORATORY FRAMATOMEANPENVmONMENTALLABORATORY (Page 11 of (Page of 1) 1) Identlficatlon MAPEP Known Framatome FramatomeIMAPEP MonthNear No. Medium Units Nuclide Results Results Ratio Evaluation May*04 04-RdF12 Filter Bq Sr-90 0.83 0.75 0.90 Agreement MaY*04 04-MaS12 Soil Bqlkg Am-241 67 59.5 0.89 Agreement Son Bqlkg Cs*134 414 455 1.10 Agreement Soil Bq/kg Cs-137 836 893 1.07 Agreement Soil Bqlkg Co-57 400 420 1.05 Agreement Soli Bqlkg Co*60 518 567 1.09 Agreement Soil Bqlkg Mn*54 485 534 1.10 Agreement Soil Bq/1<g Pu*238 35.4 38.33 1.08 Agreement Soil Bqlkg Pu-239/240 41.8 41.66 1.00 Agreement Soil Bq/kg K*40 604 666 1.10 Agreement Soil Bq/kg Sr-90 False Positive Test 2.3::1:1.2 NlA Agreement** Soli Bqlkg Zn*65 699 781 1.12 Agreement May-04 04-MaW12 Water BqJI Am-241 0.59 0.5202 0.88 Agreement Water BqJI Cs*134 208 197 0.95 Agreement Water Bq/l . Cs-137 250 232 0.93 Agreement Water BqJI Co-57 185 170.6 0.92 Agreement Water BqJI Co-60 183 157.4 0.97 Agreement Water 8qJ1 H*3 82.9 87 1.05 Agreement Water 8qll Mn-54 267 257 0.96 Agreement Water BqJI Pu-238 1.27 0.984 0.77 Waming" Water BqJI Pu-239/240 False Positive Test 0.0070::1: 0.0048 N/A Agreement.. Water BqJI Te*99 10.4 10.66 1.03 Agreement Water 8qJ1 Zn*65 208 207 1.00 Agreement
'CR 04-17
'CR 04-17 Issued Issued by by Framatome Framatome to to document document result result for for Pu*238 which which fell fell in in the the "waming" "waming" range range with with a a -20.8%
-20.8% bias bias (limit (limit of of ::t:20%
- t:20% for for waming).
waming).
"False positive "False positive results results were were measured measured by Framatoma.
by Framatoma. J*18
( c C' TABLEJ-6 TABLEJ-6 ENVIRONMENTAL RESOURCE ENVIRONMENTAL RESOURCE ASSOCIATESASSOCIATES (ERA) (ERA) PROFICIENCY TESTING PROFICIENCY TESTING PROGRAMPROGRAM -- 2004 2004 TELEDYNE BROWN TELEDYNE BROWN ENGINEERING ENGINEERING ENVIRONMENTAL ENVIRONMENTAL SERVICES SERVICES (TBE) (TBE) (Page 11 of2) (Page of2) Identification ERA Known THE THElERA ERA Month/Year No. MedIum UnIts Nuclide Result (a) ResuUs (a) Ratio Control Limits (b) Evaluation (e) May. 2004 Rad- 57 Water pCilL Sr-89 45.9 139 3,03 37.2 - 54.6 (1) pCiIL Sr-90 11.6 11.3 0.97 2.94 -20.3 A pCilL Ba-133 101 93.9 0.93 83.5 - 118 A pCilL Cs-134 50.5 43.3 0.S6 41.8 *59.2 A pCilL Cs-137 82.5 79.3 0.96 73.S - 91.2 A pCilL Co-60 41.6 42.4 1.02 32.9 -50.3 A pCiIL Zn-65 75.2 81.9 1.09 62.2*88.2 A pCilL Gr-A 38.8 39.9 1.03 22.0-55.6 A pCiIL Gr-B 59.6 62.5 1.05 42.3 -'76.9 A pCiIL H-3 30900 33500 1.08 25600 - 36200 A August. 2004 Rad-5S Water pCiIL 1-131 9.29 9.09 0.98 5.83 - 12.8 A December. 2004 Rad-59 Water pCilL Sr-89 45.7 44.0 0.96 37.0- 54.4 A pCilL Sr-90 36.6 35.3 0.96 27.9 - 45.3 A pCilL Ba-133 78.4 73.9 0.94 64.8 - 92.0 A
,,~ . pCilL Cs-134 42.9 37.8 0.88 34.2- 51.6 A
, pCilL Cs-137 60.1 58.3 0.97* 51.4 - 68.8 A
" . pCiIL Co-60 11.7 . 11.5 . '0.98* 3.04-20.4* A pCiIL Zn-65 50.9 51.3 1.01 42.1- 59.7 A pCiIL Gr-A : 31.7 23.9 0.75 18.0-45.4 W pCilL Gr-B 36.3 33.9 0.93 27.6-45.0 A pCiIL 1-131 22.1' 19.2 0.87 16.9- 27.3 A pCiIL H*3 20700 22900 1.11 17100 - 24300 A (a) Results (a) Results are are the the average average ofof three three measurements.
measurements. reported'in reported'in unitS unitS of of pC iii; pC iii; Per guidelines (b) Per (b) guidelines of of the the EPA'S EPA'S National National Standards Standards for for Water Water Proficiency Proficiency Testing Testing Criteria Criteria Document. Document. December December 1998. 1998. (e) ERA (e) ERA evaluation: evaluation: A=acceptable. A=acceptable. Reported Reported result result faUs faUs within within the the Warning Warning Limits. Limits. NA=not NA=not acceptable acceptable*.*. Reported Reported result result falls falls outside of outside of the the Control Control Limits. Limits. CE=eheck CE=eheck for for Error. Error. 'W=aeceptable
'W=aeceptable with with warning.
warning. Reported Reported 'result
'result fatls fatls within within the the Control Control Limits Limits and and outside outside of of the the Warning Warning Limit.
Limit. 1-19
.. TABLEJ*6 EN~IRONMENTAL RESOURCE RESOURCE ASSOCIATESASSOCIATES (ERA) ..
(ERA) PROFICIENCY TESTING PROFICIENCY TESTING PROGRAMPROGRAM -- 2004' 2004' .. TELEDYNE BROWN TELEDYNE BROWN ENGINEERING ENGINEERING ENVIRONMENTAL ENVIRONMENTAL SERVICES SERVICES (TBE) (TBE) (Page 22 of (Page of 2) 2) COMMENTS COMMENTS The strontium-89 amount The strontium-89 amount was was counted counted without without the the absorber. absorber. When When recounted recounted using using the the absorber, absorber, the the Sr-89 Sr-89 result result of of 41.5 pCi/1 41.5 pCi/1 agreed agreed well well with with the the ERA ERA known known value value of of 45.9 45.9 pCill. pCill. NCR NCR 04-13 04-13 generated generated by by TBE TBE to to investigate investigate condition. condition. J-20 J-20 (( (( rr
( ( ( TABLEJ-' TABLEJ-' ANALYTICS ANAL YTICS ENVIRONMENTAL ENVIRONMENTAL RADIOACfIVITY RADIOACfIVITY CROSS CROSS CHECK CHECK PROGRAM* 2004 2004 TELEDYNE QUALITY TELEDYNE QUALITY CONTROL CONTROL SPIKESPIKE PROGRAM PROGRAM TELEDYNE BROWN TELEDYNE BROWN ENGINEERING ENGINEERING ENVIRONMENTAL ENVIRONMENTAL SERVICESSERVICES (Page 1 (Page 1 of5) of5) Anafytfcs ,: Identlffcation Calculated TBE TBElAnalYtlcs MonthNear No. MedIum Units Nuclide Results Results Ratio Evaluation {1} March. 2004 E4128-396 Milk pCi/I Sr-89 103 91 0.88 A pCi/I
- Sr~90 12 13 1.08 A March. 2004 E4129-396 Milk pCi" 1--1~1 78 n 0.99 A pCi/I, Ce-141 85. n 0.91 A pCi/I Cr-51 327 340 1.04 A.
" . , ~ * ." ~ r pCi/I C5-134 90 76 0.84 A pCi/I pCfII :
Cs-137
- C0.58 185 112 176 113-0.95 1.01 A A*
pCfll 1 Mn-54 114.: 110' 0.96 A
. pCi/I
- Fe-59 57 65 1.14 A pCfII Zn-65 143 : 132: 0~92 . A pCIJI C0:.60 153 144 0.94* A I'
March,2004 E413D-396 Charcoal pCI 1-131 97 88 0.91 A March,2004 E4131-396 AP pCi, Ce-141 88 87 0.99. A pCI' Cr-51 338 325 0.96 A pCI C5-134 93 87, 0.94 A pCi C5-137 192 185 0.96 A pCI Co-58 116 117 1.01 A pCI - . Mn-S4 118,- , 105 0.89- A,' pCI Fe-59 . 59 , 59 1.00 A pCi Zn-65 . 146 179 1.21 W pCi C0-60 159 145 0.91 A pCI Fe-55 114 142 1.25 W J-21
TABLEJ-7 ANALYTICS ENVIRONMENTAL ANALYTICS ENVIRONMENTAL RADIOACflVITY RADIOACflVITY CROSS CROSS CHECK CHECK PROGRAM PROGRAM -- 2004 2004 TELEDYNE QUALITY TELEDYNE QUALITY CONTROL CONTROL SPIKE SPIKE PROGRAM PROGRAM TELEDYNE BROWN TELEDYNE BROWN ENGINEERING ENGINEERING ENVIRONMENTAL ENVIRONMENTAL SERVICES SERVICES (Page 2 (Page 2 of5) of5) Analytics Identification Calculated TBE TBEIAnalytlcs MonthlYear No. Medium Units Nuclide Results Results Ratio Evaluation {1} June, 2004 E4213-396 Milk pCUI Sr-89* 87.7 77.9 0.89 A Sr-90 12.7 12.0 0.94 A June,2004 E4214-396 Milk pCUI 1-131' 58.2 53.7 0.92 A pCUI Ce-141 157 145 0.92 A pCUI Cr-51 228 212 0.93 A pCUI Cs-l34 101 85.2 0.84 A pCUI Cs-137 156 145 0.93 A pCUI Co-58 46.2 45.7 0.99 A pCUI Mn-54 70.5 68.2 0.97 A pCUI Fe-59 44.5 44.4 1.00 A pCUI 20-65 99.3 102 1.03 A pCUI Co-60 172 162 0.94 A June. 2004 E4216-396 AP pCI Ce-141 118 116 0.98 A pCi Cr*51 172 160 0.93 A pCI Cs-l34 76.3 68.6 0.90 A pCI Cs*137 118 108 0.92 A pCI Co-58 39.4 33.1 0.84 A pCI Mn-54 53.3 51.1 0.96 A pCI Fe*59 33.6 44.0 1.31 (2) pCI Zn-65 . 75.1 69.1 0.92 A pCI Co-60 130 ..123 0.95 A pCI Fe-55 104 100 0.96 A June. 2004 E4215-396 Charcoal pCI 1*131 82.0 71.8 0.88 A I J*22 ( ( ( r
( ( c TABLEJ*7 ANALYTICS ANAL YTICS ENVIRONMENTAL ENVIRONMENTAL RADIOACfIVITY RADIOACfIVITY CROSS CROSS CHECK CHECK PROGRAM PROGRAM -- 2004 2004 TELEDYNE QUALITY TELEDYNE QUALITY CONTROL CONTROL SPIKE SPIKE PROGRAM PROGRAM TELEDYNE BROWN TELEDYNE BROWN ENGINEERING ENGINEERING ENVIRONMENTAL ENVIRONMENTAL SERVICESSERVICES (Page 3 (Page 3 of5) of5) Analytlcs Identification Calculated TBE TBElAnalytfcs MonthNear No. Medium UnIts Nuclide Results Results Ratio Evaluation {1} September, 2004 E4323-396 Milk pCIII Sr~89 102 94 0.92 A pCIII Sr-90 24.5 24.0. 0.98 A September, 2004 E4324-396 Milk pCIII 1-131 83.5., 81.9 0.98 A pCIII Ce-141 235 214* 0.91 A pCIII Cr-51 2tO 196 0.93 A
. pCIII Cs-134 . 90.6 77.3 0.85 A pCIII Cs-137 202 192 0.95 A pCIII C()-58 ) 89.0 86.2* 0.97 A:
pClII . Mn-54. 171 163, 0.95 A pCIII* Fe-59** 86.1 '87.4, 1.02 A. pCIII ZO-6!>. 167 168, 1.01 A pClII C0-60* 118 108 0.92 A September, 2004 E4326*396 AP Filter pCI Ce-141 148 149 1.01 A pCI Cr-51 132 122 0.92 A pCi Cs-134 57.1 50.3 0.88 A pCI C8-137 127 112 0.88 A pCI Co-58 56.0 55 0.98 A pCI Mn-54 108.0 102 0.94 A pCi Fe-59 54.2 48 0.88 A pCI Zn*65 106 111 1:05 A pCI C0-60 74.1 . 69 .. 0.93 A September, 2004 E4325*396 Charcoal pCI 1-131
.74.9 70.3 0.94 A
,j
; t
)*23
TABLEJ*7 ANALYTICS ANAL YTICS ENVIRONMENTAL ENVIRONMENTAL RADIOACfIVITY RADIOACfIVITY CROSS CROSS CHECK CHECK PROGRAM PROGRAM -- 2004 2004 TELEDYNE QUALITY TELEDYNE QUALITY CONTROL CONTROL SPIKE SPIKE PROGRAM PROGRAM TELEDYNE BROWN TELEDYNE BROWN ENGINEERING ENGINEERING ENVIRONMENTAL ENVIRONMENTAL SERVICES SERVICES (Page 44 of5) (Page of5) Analytlcs Identification Calculated TBE TBElAnalytlcs Month/Year No. Medium Units Nuclide Results Results Ratio Evaluation ~1} October, 2004 E4407-396 Milk pCiII Sr-89 98.6 91.7 0.93 A pCiII Sr*90 11.3 11.9 1.05 A October, 2004 E4408-396 Milk pCUl 1-131 66.7 58.3 0.87 A pCiII Ce*141 155 140 0.90 A pCiII Cr-51 379 374 0.99 A pCiII Cs-l34 170 143 0.84 A pCUl Cs-137 126 120 0.95 A pCiII Co-56 146 140 0.96 A pC ill Mn-54 136 135 0.99 A pCiII Fe-59 *121 124 1.02 A pCiII . Zn~65 196 196 1.01 A pCiII C0-60 175 166 0.95 A October, 2004 E441D-396 AP Filter pCi Ce-141 79.1 n.o 0.97 A pCi Cr-51 187 156 0.83 A pCi C~-l34 83.5 76.6 0.92 A pCI Os-137 62.0 58.9 0.95 A pCI Co-58 71.8 68.6 0.96 A pCi Mn-54 66.7 63.2 0.95 A pCi Fe-59 59.7 652 1.09 A pCI Zn-65 96.3 99.7 1.04 A pCi C0-60 85.9 80.1 0.93 A October, 2004 E4409A-396 Charcoal pCi 1*131 83.3 80.9 0.97 A ( c ( rr
( ( ( TABLEJ*7 ANALYTICS ENVIRONMENTAL ANALYTICS ENVIRONMENTAL RADIOACfIVITY RADIOACfIVITY CROSS CROSS CHECK CHECK PROGRAM PROGRAM -- 2004 2004 TELEDYNE QUALITY TELEDYNE QUALITY CONTROL CONTROL SPIKE SPIKE PROGRAM PROGRAM TELEDYNE BROWN TELEDYNE BROWN ENGINEERING ENGINEERING ENVIRONMENTAL ENVIRONMENTAL SERVICES SERVICES (page 5 (page 5 of 5) of 5) COMMENTS COMMENTS 1 Analytics evaluation based on on TBE TBE Internal ac limits: Internal ac limits: A= A= Acceptable. Acceptable. Reported Reported result result falls falls within within ratio ratio limits limits of of 0.80-1.20. 0.80-1.20. W-Acceptabte W-Acceptabte withwith warning. warning. Reported Reported result result falls falls within within 0.70-0.80 0.70-0.80 or or 1.20-1.30. 1.20-1.30. N N== Not Not Acceptable. Acceptable. Reported Reported result falls result falls outside outside the the ratio ratio limits limits of of < 0.70 and>
< 0.70 and> 1.30.
1.30. 2 2 The Analytics filter The Analytics filter had had very very low low activity activity and and was was counted counted longer longer than than two two days. days. This This resulted resulted InIn poor poor accuracy accuracy asas demonstrated demonstrated by by the very the very large large error error term. term. Dan Dan Montgomery Montgomery of of Analytlcs Analytlcs concurred concurred that, that, with with the the low low counts counts and and large large error, error, the the results results were were reasonably reasonably accurate and accurate and would would not not be be considered considered a a failed failed cross cross check check at at 1.31 1.31 for for an an environmental environmental level level sample. sample. NCR 04-16 NCR 04-16 generated generated byby TBE TBE toto investigate investigate condition. condition. J-25 J-25
(( c c C C TABLEJ*8 PPL REMP LABORATORY PPL REMP LABORATORY SPIKE SPIKE PROGRAM PROGRAM ANALYTICS ANAL YTICS ENVIRONMENTAL ENVIRONMENTAL RADIOACTIVITY RADIOACTIVITY ,CROSS ,CROSS CHECK CHECK PROGRAM PROGRAM -- 2004 2004 TELEDYNE BROWN TELEDYNE BROWN ENGINEERING ENGINEERING ENVIRONMENTAL ENVIRONMENTAL SERVICESSERVICES (Page 11 of6) (Page of6) Identification Anatytlcs TBE TBE!Analytlcs MonthNear No." Medium Units Nuclide Calculated Results {a} Results {a} Ratro Evaluatlon~21 March-04 E4067-186 Sediment pClJkg Ce-141 150'+/- 5 187 +/- 29 1.25 A pClJkg Cr-51 576 +/- 19 622 +/- 134 1.08 A pClJkg Cs-l34 159 +/-5 150'+/- 12 0.94 A pClJkg Cs-137 432 +/- 14 453 +/-20 1.05 A pCi/kg Co-58, 198 +/- 7: 212 +/- 18 1.07 A pCi/kg Mn-54 201 +/-7 218'+/- 18' 1.08 A pClJkg Fe-59 100,+/-3 113:£25 1.13 A pClJkg Zn*65 252 +/-'8 305'+/-28 1.21' A
;. r'!' .::.; ,- . ,~ ~; , . pClJkg Co-60, 270'£9' 282'+/-'13 1.04 A' March-04 E4063-186 Milk pC11I ,1-,131 91 +/-3 70'£ 16 o.n W pCIII Ce-141 95 +/-'3' 97 +/- 15 1.02 A pCi/I Cr-51 363 +/- 12 260 +/- 91 0.72 W pCi/I Cs-134 100 +/-3 78 +/-8 0.78 W pC11I Cs-137 206 +/-7 192 +/- 18 0.93' A pCiIJ Co-58 125 +/-4 123 +/-14 0.98 A pCiIJ Mn*54 127 +/-4 114 +/- 14 0.90 A pCiIJ Fe-59 63 +/-2 65 +/- 16 1.03 A pC11I Zn-65 159 +/-5 143 +/- 24 0.90 A pCiIJ Co-60 170 +/- 6 153 +/- 11 0.90 A March-04 E4064*186 AP Filter pCI' Ce-14f'
-, ., 60:i: 2 n+/-13 1.28 W
, , pCI Cr-51 231 +/-8 228+/-n 0.99' A pCI CS-134 64 +/-2 62 +/-8 0.97 A pCI Cs-137'. ' 131 +/- 5 122 +/- 12 0.93 A pCI. Co-58 79,+/-3, 73 +/-9 0.92 A
, pCI Mri*S4 81 +/- 3, ,74.3 +/- 1 0.92 A pCl 'Fe-59 40 +/- 1 52.6 +/- '14 ' 1.32 N(3) pCi' Zn*65 ' , . '101 +/-'4 109 +/- 18 1.08 A pCI Co-60 108 +/-4 108 +/- 9 1.00 A (a) Counting (a) Counting error error isis two two standard standard deviations.
deviations. J.26 J.26
TABLEJ-8 TABLEJ-8 PPL REMP PPL REMP LABORATORY LABORATORY SPIKE SPIKE PROGRAM PROGRAM ANALYTICS ANAL YTICS ENVIRONMENTAL ENVIRONMENTAL RADIOACTIVITY RADIOACTIVITY CROSS CROSS CHECK CHECK PROGRAM PROGRAM -- 2004 2004 TELEDYNE BROWN TELEDYNE BROWN ENGINEERING ENGINEERING ENVIRONMENTAL ENVIRONMENTAL SERVICESSERVICES (Page 22 of (Page of 6) 6) Identification Analytlcs TBE TBElAnalytics MonthIYear No. Medium Units Nuclide Calculated Results (a) Results (a) Ratio Evaluatlon(2) March-04 E4065-186 AP Filter pCI Ce-141 61 +/- 2 62.7 +/- 12 1.03 A pCI Cr-51 235+/- 8 234 +/- 72 1.00 A pCI Cs-l34 65+/-2 60.6:t 6 0.93 A pCI CS-137 134 +/- 5 129:t 11 .0.96 A pCI Co-58 81 :t 3 n.8 +/- 10 0.96 A pCI Mn-54 82:t 3 73+/- 9 0.89 A pCI Fe-59 41 :t 1 39:t 12 0.95 A pCI 20-65 103 +/-4 92:t 16 0.89 A pCI Co-60 110 +/- 4 98 +/- 8 0.89 A March-04 E4066-186 AP Filter pCI Ce-141 62:t 2 66.6 +/- 13 1.07 A pCI Cr-51 237+/-8 220 +/- 62 0.93 A pCI Cs-l34 65 +/-2 58.4:t 7 0.90 A pCI Cs-137 135 +/- 5 126 :t12 0.93 A pCI Co-58 82 +/-3 76 +/- 12 0.93 A pCI Mn-54 83:t 3 83:t 12 1.00 A pCI Fe-59 41 +/- 1 44.4 +/- 13 1.08 A pCI 20-65 104 +/- 4 115 +/-*14 1.11 A pCI Co-60 111:t4 112 +/- 17 1.01 A March-04 E4068-186 Water pCI/I H*3 4700 +/- 300 5070 +/- 163 1.08 A June-04 E4202-186 Charcoal pCI 1-131 82.9 :i:3 84.6:t 5 1.02 A June-04 E4203-186 Charcoal pCI 1-131 n-i.3 82.1 :t 3 1.07 A June-04 E4204-186 Charcoal pCI 1-131 89.B:t 3 93.9:t 5 1.05 A c (a) Counting (a) Counting error error is is lWO standard deviations. lWO standard deviations. J-27 (( (( c J-27 r
(( c c C C TABLEJ*8 PPL REMP LABORATORY PPL REMP LABORATORY SPIKE SPIKE PROGRAM PROGRAM ANALYTICS ANAL YTICS ENVIRONMENTAL ENVIRONMENTAL RADIOACTIVITY RADIOACTIVITY CROSS CROSS CHECK CHECK PROGRAM PROGRAM -- 2004 2004 TELEDYNE BROWN TELEDYNE BROWN ENGINEERING ENGINEERING ENVIRONMENTAL ENVIRONMENTAL SERVICES SERVICES of 6) (page 33 of Identification Analytlcs ' TBE TBEIAnalytlcs MonthlYear No. Medium Units Nuclide Calculated Results (a} Results (a} RatTo Evalustfon(2} September-04 E4307-186 Milk pCI/1 1-131 76 +/-3 0.00 (1) pCI/1 Ce-141 518 +/- 17 0.00 (1) pC11I Cr*51 463 +/- 15 0.00 (1) pCI/1 Cs*134 200 +/-7 0.00' (1) pCI/1 Cs-137. 445 +/- 15 0.00 (1) pCI/1 Co-58 196 +/- 7 0.00 (1) pCI/1 Mn*54 376+/-'13 0.00 (1) pCl/1 Fe-59: 190+/- 6. 0.00 (l) pCl/1 Zn*65 370+/- 12,' 0.00, (1" l' \,~ *
" I,,"$., , r "
' . pCI/1 Co-SO i 260 +/-9 ' " .' 0.00* (1)
September-04 E4308*186 Charcoal pCL 1*131'* 74.7 +/- 3' 77+/- 2 1.04 A September-04 E4309-186 Charcoal pCI 1-131 83.1 +/- 3 89 +/- 4 1.07 A September-04 E4310-186 Charcoal pCI 1-131 71.5 +/- 2 78'+/-3 1.09 A October*04' E4339*186 Milk pCI/1 1-131 79 +/-3 78.4 +/- 3 0.99 A' pCI/1 Ce*141 89,+/-3. 81.2+/-6 ' 0.91 A pCIII, Cr*S1 2790 +/- 93 2560 £63 0.92 A pCI/1. Cs*134 69 +/-2 58.4 +/-'4 0.85 A pCI/1 Cs-137 158 +/- 5 ' 140 +/- 7 0.89 A pCI/1' CO:-S8: SO+/-2 46.6+/- 6 0.93 A pCI/1 Mn-54 124 +/-'4 ' 116 +/- 6 0.94 A pCl/1 ' Fe-59 40 +/- 1 40.3 +/- 7 1.01 A pCI/1 Zn-65 .119 +/-.,. 116 +/- 10 0.97 A pCI/1 " Co-60 91.+/- 3. ; ~ .' . 84.6 +/-'~ 0.93 A October-04 E4341-186 Water 'pC~ H*3 2180 +/- 73 2180 +/- 172 1.00 A (a) Counting (a) Counting error error is is two two standard standard deviations. deviations. J*28
TABLEJ-8 TABLEJ-8 PPL REMP PPL REMP LABORATORY LABORATORY SPIKE SPIKE PROGRAM PROGRAM ANALYTlCS ANAL YTlCS ENVIRONMENTAL ENVIRONMENTAL RADIOACfIVITY RADIOACfIVITY CROSS CROSS CHECK CHECK PROGRAM PROGRAM -- 2004 2004 BROWN ENGINEERING TELEDYNE BROWN TELEDYNE ENGINEERING ENVIRONMENTAL ENVIRONMENTAL SERVICES SERVICES (Page 44 of (Page of 6) 6) Identification Analytlcs TBE TBElAnalytics MonthlYear No. Medium Units Nuclide Calculated Results {a} Results {al Ratio Evaluatlon{2} December-04 E4413-186 Milk pCVI 1-131 71-+/- 2 57.5 +/- 2 0.81 A pCVI " Ce-141 167 +/-.8 157 +/- 10 0.94 A pCVI Cr-51 410 +/- 21 404 +/- 46 0.99 A pCVI Cs-134 184 +/- 9 160 +/- 5 0.87 A pCVI Cs-137 136 +/- 7 136 +/- 7 1.00 A pCVI Co-58 158 +/- 8 153 +/- 8 0.97 A pCVI Mn*54 147 +/- 7 148 +/- 7 1.01 A pCiII Fe-59 131 +/- 7 129 +/- 10 0.98 A pCVI Zn*65 212 +/- 11 212 +/- 14 1.00 A pCVI Co-GO 189 +/- 9 180 +/- 6 0.95 A December-04 E4414-186 AP Filter pCI Ce-141 115+/-4 112 +/- 8 0.97 A pCI Cr-51 271 +/- 10 290 +/- 47 1.07 A pCI Cs-134 121 +/- 4 109 +/-4 0.90 A pCI Cs-137 90+/-3 85.7 +/- 6 0.95 A pCI Co-58 104 +/- 4 93.7 +/- 6 0.90 A pCI Mn*54 97 +/- 3 - 88+/- 7 *0.91 -A pCI Fe-59 87 +/-3 85.2 +/- 9 0.98 A pCI Zn-65 140 +/- 5 131 +/- 11 0.94 A pCI Co-60 125 +/- 4 122 +/- 5 0.98 A December-04 E4415*186 AP Filter pCI Ce-141 99 +/-3 89.2 +/- 8 0.90 A pCI Cr-51 234 +/-8 223 +/- 38 0.95 A pCI Cs-l34 105 +/-4 97.1 +/- 4 0.92 A pCI Cs-137 78 +/- 3 72.3 +/- 5 0.93 A pCI Co-58 90 +/- 3 81.5 +/- 6 0.91 A pCI Mn*54 84 +/-3 80.2 +/- 6 0.95 A pCI Fe-59 75 +/-3 81.4 +/- 10 1.09 A pCI Zn*65 121"+/- 4 114 +/- 10 0.94 A pCI Co*GO 108 +/-4 102 +/-5 0.94 A (a) Counting (a) Counting error error is is two two standard standard deviations. deviations. J*29 (( (( ((
(( cc cc TABLEJ.8 TABLEJ.8 PPL REMP LAB PPL REMP LAB ORA ORATORY TORY SPIKE SPIKE PROGRAM PROGRAM ANALYTICS ANAL YTICS ENVIRONMENTAL ENVIRONMENTAL RADIOACTIVITY RADIOACTIVITY CROSS CROSS CHECK CHECK PROGRAM PROGRAM -- 2004 2004 TELEDYNE BROWN TELEDYNE BROWN ENGINEERING ENGINEERING ENVIRONMENTAL ENVIRONMENTAL SERVICES SERVICES (pageS of (pageS of 6) 6) Identification Analytlcs TBE TBE/Analytlcs MonthNear No. Medium Units Nuclide Calculated Results {a} Results {a} Ratio Evaluatlon(2) Dacember-04 E4416-186 AP Riter pCi Ce-141 128 +/- 5 122 +/- 15 0.95 A pCi Cr-51 301 +/- 11 277 +/- 85 0.92 A pCI Cs-134 135 +/- 5 124 +/- 10 0.92 A pCI Cs-137 100 +/- 4 101 +/- 14 1.01 A pCI Co-56 116 +/- 4 102 +/- 12 0.8a A pCl Mn-54 108 +/- 4 113 +/- 12 1.05 A pCI Fe-59 96 +/-3 96 +/- 16 1.00 A pCI Zn-65 155 +/- 5 145 +/- 25 0.94 A pCI C0-60 139 +/- 5 121 +/- 11 0.87 A _r _r
' ,~ : .. .'
" " ,~
\
(a) Counting (a) Counting error error is is two two standard standard deviations. deviations. J-30 J-30
TABLEJ-8 TABLEJ-8 PPL REMP LABORATORY PPL REMP LABORATORY SPIKE SPIKE PROGRAM PROGRAM ANALYTICS ANAL YTICS ENVIRONMENTAL ENVIRONMENTAL RADIOACTIVITY RADIOACTIVITY CROSS CROSS CHECK CHECK PROGRAM PROGRAM -- 2004 2004 TELEDYNE BROWN TELEDYNE BROWN ENGINEERING ENGINEERING ENVIRONMENTAL ENVIRONMENTAL SERVICES SERVICES (Page 60f6) (Page 60f6) COMMENTS COMMENTS 1 1 Milk sample Milk sample E4307-186 E4307-186 could could not not be be analyzed analyzed for for gamma gamma and and 1-131 1-131 (low (low level) level) analyses analyses due due to to curdled curdled milk. milk. 2 2 TBE evaluation: TBE evaluation: A A== acceptable, acceptable, W W== acceptable acceptable with with warning, warning, N N= = not not acceptable. acceptable. 3 3 NCR 05-04 NCR 05-04 generated generated by by Teledyne Teledyne to to document document condition. condition. J*31 (( (( ((
(( cc C C TABLEJ-9 TABLEJ-9 ENVIRONMENTAL MEASUREMENTS DOE* ENVIRONMENTAL MEASUREMENTS LABORATORY LABORATORY (EML)(EML) QUALITY ASSESSMENT QUALITY ASSESSMENT PROGRAM PROGRAM (QAP) (QAP) TELEDYNE BROWN TELEDYNE BROWN ENGINEERING ENGINEERING ENVIRONMENTAL ENVIRONMENTAL SERVICES SERVICES (Page 11 of of 2) IdentJfJcatJon EMLKnown TBE TBElEML MonthNear No. Medium Units Nuclide Result Results Ratio Evaluatlon{3} March,2004 QAP60 AP Filter Bq Co-60 35.4 33.5 0.95 A (QAP 0403) Bq Sr-90 1.76 1.8 1.02 A Bq Cs-134 18.2 18.7 1.03 A Bq Cs-137 26.4 24.8 0.94 A Bq Gr-A 1.2 1.8 1.50 (1) Bq Gr-B 2.85 2.88 1.01 A Soil Bqlkg K-40 539 583 1.08 A
.~': -:' ; ,*'; ,," ~ . , f , *** ~,' , I * ~
Bqikg - _"-Sr-90 ":iL "'50r' " . 42.1 0.83 A Bqlkg Cs-137 1323 1429 1.08 A Bqlkg 81-212 50.43 52.6 1.04 A
'Bqlkg ,. Pb-212 47.73 50.1 1.05 A Bqlkg 81-214 58.4 57.6 0.99 A Bqlkg Pb-214 61.0 61.4 1.01 A Bqlkg ., Ac-228 49.0 49.4 1.01 A Bqlkg Th-234 84.0. . 114.9 ,1.37 ' (2)
Vegetation Bqlkg K*40 720.0 807.5 1.12 A Bqlkg Co-60 .. 14.47 14.2 0.98 A 8q1kg Sr-90 734.0 685 0.93 A Bqlkg Cs*137 584.67 637.3 1.09 A Water BqJ1 Co-60 163.2 159.7 0.98 A BqJ1 Sr-gO. 4.76' 4.74 1.00 A BqJ1 Cs-137 51.95 50.6 0.97 A
" BqJ1 Gi*A 326.0 394.0 1.21 W Bqll Gr-B " 1170.0 1200.0 1.03 A 1-32 1-32
TABLEJ*9 DOE -- ENVIRONMENTAL DOE ENVIRONMENTAL MEASUREMENTS MEASUREMENTS LABORATORY LABORATORY (EML) (EML) QUALITY ASSESSMENT QUALITY ASSESSMENT PROGRAM PROGRAM (QAP) (QAP) TELEDYNE BROWN TELEDYNE BROWN ENGINEERING ENGINEERING ENVIRONMENTAL ENVIRONMENTAL SERVICES SERVICES (Page 22 of (Page of 2) 2) COMMENTS COMMENTS 1 1 Incorrect efficiency Incorrect efficiency used. used. When When recalculated recalculated with with the the correct correct efficiency, efficiency, the the Gross Gross Alpha Alpha activity activity of of 1.16 1.16 8q1fi1ter 8q1fi1ter compared compared well well with with the the value of 1.2 value of 1.2 8q1fi1ter. 8q1fi1ter. NCR NCR 04-14 04-14 generated generated byTBE byTBE to to investigate investigate condition. condition. 2 2 DOElEML evaluated DOElEML evaluated as as acceptable acceptable at at the the calculated calculated ratio. ratio. 3 3 DOElEML evaluation: DOElEML evaluation: A=acceptable, A=acceptable, W=acceptable W=acceptable withwith warning. warning. N=nol N=nol acceptable. acceptable. J-33 J-33 (( (( ((
( c C TABLEJ*I0 DOE*MAPEP' MIXED ANAL MIXED Yrn PERFORMANCE ANALYrn PERFORMANCE EVALUA EVALUAnON nON PROGRAM PROGRAM TELEDYNE BROWN TELEDYNE BROWN ENGINEERING ENGINEERING ENVIRONMENTAL ENVIRONMENTAL SERVICES SERVICES (TBE) (TBE) (Page 11 of3) (Page of3) , : ,' " Identification " MAPEP Known THE MonthlYear No. Medium Units Nuclide Result ,Results Control LImits Evaluatlon{4} January, 2004 03-W11 Water pCI/J Cs-134 8.70E+03 7.81E+03 6081 '*11,313 A pCI/J Cs-137 3.35E+03 3.21E+03, 2346 - 4357 A pCI/J, Co-57, 4.68E+03 4.43E+03 3273- 6078 A pCW Co-60 3.29E+03 3.27E+03 2304- 4279 A
~ "* I ,. pCIJI H-3, ~ 1.02E+04 1.15E+04 7170 ~ 13,316 A pCI/J Fe-55 3.54E+03 3.44E+03 2478'- 4603 A pCI/J Mn-S4 4.19E+03 4.12E+03 2932- 5446 A' pCI/J NI-63 , ' .',r 1.99E+03' 3.48 E+3, 1394- 2589 N(1) pCI/J Zn:S5 ",,, 8.65E+03: 8.20E+03- 6054 ; 11,243 A, pCI/J Sr-90-';'1 4.78E+02' 4.43E+02' 334.9 - 621 ~9 A' pCI/J Tc-99 , 778.4 ' '643.2- 545-1012 A pCI/J Pu-238 , :40.3' " . '33.8 28.1 - 52.4 A pCiII PU-239/240 64.6 57.8' 45.1 - 84.1 A-pC11I U-234/233 63.5 67 44.6- 82.7 A pCIJI U-238 ,S5.7 ,65.7 46 -85.4 A July. 2004 MaW12 Water pCiII Am-241 15.9 16.8 11.4 - 21.1 A.
pC11i Cs-134 5.62E+03 4.78E+03 3925 -7308 A pCIJI Cs-137 6.76E+03 6.41E+03 4730- 8784 A pCiII Co-SO 4.41E+03 4.32E+03 3084- 5725 A pCiII H-3' " 2.24E+03 2.95E+03 1570 - 2916 N(2) pCI/J Mn-54 .,7.22E+03 7.08E+03 5051 - 9381 A pCIII NI-63 2.70E+03 3.76E+03 1892 - 3514 N(3) pCIII Sr-90 2.00E+02 1.84E+02 132- 246 A pCIJI Tc-99 281 242 189- 351 A pC11I Zn-65 5.62E+03 5.8SE+03 3935-7308 A "CiII Pu-238 '[ 3.35E+01 '2.97E+01 ' 22.7 - 42.2 A pCIII , . U-234/233 ." 3.24E+00 ' , *4.00E+00 2.16- 4.32 W pCill U-238 .
.,.t*. , ' . '25.4 2S.4 17*31.S A J-34 J-34
TABLEJ~10
. DOE*MAPEP MIXED ANALYTE MIXED ANAL YTE PERFORMANCE PERFORMANCE EVALUATION EVALUATION PROGRAM PROGRAM TELEDYNE BROWN TELEDYNE BROWN ENGINEERING ENGINEERING ENVIRONMENTAL ENVIRONMENTAL SERVICES SERVICES (TBE)
(TBE) (Page 2 (Page 2 of3) of3) Identification MAPEl' Known THE MonthlYear No. Medium Units Nuclide Result Results Control Limits Evaluatlon{4l July. 2004 GrW12 Water pCiII Gr-A 3.35E+01 2.26E+01 >0.0- 64.9 A pCiII Gr-B 1.10E+02 1.34E+02 55.4-166.2 A July. 2004 RdF12 AP Bq Am-241 .2.7 2.6 1.89 - 3.51 A Bq Cs-134 7.84E+01 5.92E+01 54.9 - 101.9 W Bq Cs-137 5.30E+01 5.05E+01 37.8-70.3 A Bq Co-60 . 6.35E+01 6.16E+01 43.5- 80.8 A Bq Mn-54 8.19E+01 8.27E+01 56.8-10S.4 A Bq Sr-90 2.24E+01 2.46E+01 15.1 - 28.1 A Bq Zn-65 1.11E+02 1.22E+02 75.7 *140.5 A Bq Pu-238 3.51 3.43 2.43 -4.59 A Bq Pu-239/240 2.43 2 1.62-3.24 A Bq U-234/233 5.68 5.92 4.0S-7.30 A Bq U-238 5.95 5.65 4.05-7.84 A July. 2004 GrF12 AP Bq Gr-A 1.00E+01 3.41E+00 >0.0-21.6 A Gr-B 3.27E+01 3.62E+01 16.2 :'-48.6 A July, 2004 MaS12 Soit pCVkg Am-241 1.81E+03 1.73E+03 1267*2353 . A pCVkg Cs-134 1.12E+04 8.86E+03 7840 - 14,560 W pCVkg Cs'*137 2.26E+04 2.12E+04 15,820 - 29A05 A pCVkg, Co-60 1.40E+04 1.38E+04 9800.-.18.200 A pCiII<g Mn-54 1.31E+04 1.29E+04 9170 -17,030 A pCVkg Ni-63 9.6SE+03 7.92E+03 6755 - 12,545 A pCiII<g Pu-238 9.57E+02 7.32E+02 670*1244 W pCVkg Pu-239/240 1.13E+03 64.6 791 - 1300 N(5) pCiII<g K-40 1.63E+04 1.6SE+04 11 ,427 - 21,222 A pCVkg Te-99 3.18E+03 1.41E+03 2226 - 4134 N(6) pCiII<g U-234/233 1.00E+03 3.62E+02 700*1300 N(5) pCiII<g U-238 1.05E+03 3.59E+02 735-1365 N(5) pCVkg Zn-65 1.89E-+;04 1.96E+04 13,230
- 24,570 A
).35
).35
(( (( C.C.
c c c TABLEJ*I0 DOE*MAPEP MIXED ANAL MIXED ANALYTE YTE PERFORMANCE PERFORMANCE EV EVALUATION ALUATION PROGRAM PROGRAM TELEDYNE BROWN TELEDYNE BROWN ENGINEERING ENGINEERING ENVIRONMENTAL ENVIRONMENTAL SERVICES SERVICES (TBE) (TBE) (Page 3 (Page 3 of of 3) 3) COMMENTS COMMENTS 1 1 Ni-63 result Ni-63 result determined determined toto be be an an anomaly, anomaly, specific specific only only to to this this sample. sample. NCR NCR 04*11 generated generated byby Teledyne Teledyne to to document document condition. condition. 2 2 All raw data All raw data looked looked normal normal for for the the sample. sample. Evaluating Evaluating thethe results results based based onon the +/- 541 the +/- 541 pCIII pCIII uncertainty, uncertainty, the the result result easily easily overlaps overlaps the the known value known value at at the the 95% 95% confidence confidence level. level. The The sample sample waswas rerun rerun with with aa larger larger aliquot aliquot to to improve improve accuracy accuracy and and lower lower thethe uncertainty. uncertainty. The rerun The rerun result result of of 2,605 2,605 +/-+/- 209 209 pCIII pCIII agrees agrees with with the the known known value value of of 2,240 2,240 pCIII. pCIII. NCR NCR 04*19 generated generated byby Teledyne Teledyne to to document document condition. condition. . 3 The rerun The rerun result result of of 2,700 2,700 pCIII pCIII agrees agrees well well with with the the known known value value of of 2,702 2,702 pCIII. pCIII. NCR NCR 04-18 04-18 generated generated by by TeJedyne TeJedyne toto document document condition. condition. 4 4 DOEIMAPEP evaluation: DOEIMAPEP evaluation: A=acceptable, A=acceptable, .W=acceptable
.W=acceptable with with warning, warning, N=not N=not acceptable.
acceptable. 5 5 Non-leachable U Non-leachable U and and Pu Pu were were present present in in the the soil. soil. The The sample sample waswas rerun rerun and and the the results results agreed agreed with with the the known known values. values. NCR NCR 04-20 04-20 generated generated by by Teledyne Teledyne toto document document condition. condition. 6 6 Special rinses Special rinses for for samples samples with with high high Uranium Uranium andand Co-60 Co-60 was was used used onon these these samples. samples. Reran Reran without without these these rinses rinses yielded yielded Tc-99 results of Tc-99 results of 2,757, 2,757, 2,311, 2,311, and and 2,651 2,651 pClIKg pClIKg which which were were within within the the acceptance acceptance criteria. criteria. NCR NCR 04-21 04-21 generated generated by by Teledyne Teledyne toto document condition. document condition. 1-36}}